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HomeMy WebLinkAboutMC-7661 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 ORDINANCE NO. MC-766 URGENCY ORDINANCE OF THE CITY OF SAN BERNARDINO ADDING CHAPTER 17.05, SECTIONS 17.05.010 AND 17.05.020, TO THE SAN BERNARDINO MUNICIPAL CODE REQUIRING LAND USE APPLICATIONS FOR HAZARDOUS WASTE FACILITIES TO COMPLY WITH THE COUNTY HAZARDOUS WASTE MANAGEMENT PLAN. THE MAYOR AND COMMON COUNCIL OF THE CITY OF SAN BERNARDINO DO ORDAIN AS FOLLOWS: SECTION 1. Chapter 17.05, Sections 17.05.010 and 17.05.020, are hereby added to the San Bernardino Municipal Code to read as follows: "Chapter 17.05 HAZARDOUS WASTE MANAGEMENT PLAN Sections: 17.05.010 Applicability. 17.05.020 Hazardous Waste Facility Defined. 17.05.010 Applicability. Any application for a zoning amendment, subdivision, conditional use permit, or variance for a hazardous waste facility shall comply with Chapter 5 of the County Hazardous Waste Management Plan, entitled "Siting of Specified Hazardous Waste Facilities" attached as Attachment "1" and incorporated herein by reference, in addition to complying with all other applicable City ordinances. 17.05.020 Hazardous Waste Facility Defined. Hazardous Waste Facility, as defined in California Health and Safety Code Section 25117.1, means all contiguous land and structures, other appurtenances, and improvements on the land used for the treatment, transfer, storage, resource recovery, disposal, or recycling of hazardous waste. A hazardous waste facility may consist of one or more treatment, transfer, storage, HE/dys/hazwaste.ord 1 December 7, 1990 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 resource recovery, disposal, or recycling hazardous waste management units, or combinations of these units." SECTION 2. This is an urgency ordinance which will take effect immediately upon its adoption. The reason for the urgency is that hazardous waste facilities will have a deleterious effect on surrounding land uses, the environment, and nearby businesses and residents if regulations are not in place which will ensure that they are located only in appropriate sites, with adequate mitigation of all adverse environmental impacts, and with comprehensive procedures and standards for evaluating facility applications. This urgency ordinance is necessary to protect the public health, safety and welfare. I HEREBY CERTIFY that the foregoing ordinance was duly adopted by the Mayor and Common Council of the City of San Bernardino at a regular meeting thereof, held on the 17th day of December 1990, by the following vote, to wit: Council Members: ESTRADA REILLY FLORES MAUDSLEY MINOR POPE-LUDLAM MILLER AYES NAYS ABSTAIN X X X X X ~- ,~~.c_h..n_-~~ ~t.c,~-~''~ Cit Clerk C HE/dys/hazwaste.ord December 7, 1990 2 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 `~~~~~~~ URGENCY ORDINANCE ADDING CHAPTER 17.05, SECTIONS 17.05.010 AND 17.05.020, TO COMPLY WITH THE COUNTY HAZARDOUS WASTE MANAGEMENT PLAN. The foregoing ordinance is hereby approved this ~ Jft~ day of December 1990. j~~ . ~ ~/~ ~ ..~: --~' . R. Ho omb, Mayof" City of 'San Bernardino Approved as to form and legal content: JAMES F. PENMAN, City Attorney HE/dys/hazwaste.ord 3 December 7, 1990 SAN BERNARDINO COUNTY aAZARDOtJS WASTE w.u ._..::..MANAGEMENT PLAN t :~~. r; h?TAc rIN~EN T l~ I~ COUNTY OF SAN BERNARDINO BOARD OF SUPERVLSORS MARSHA TUROCI FIRST DISTRICT JON D. MIKELS SECOND DISTRICT BARBARA CRAM RIORDAN THIRD DISTRICT LARRY WALKER FOURTH DISTRICT ROBERT L. HAMMOCK FIFTH DISTRICT PLANNING GAREY TEETERS, Chairman • RAY FERGUSON, Vice Chairman WILLIAM DEGROOT MICHAEL DOMBROWSKI RON DOSSEY RUSSELL EASTERDAY SUSANNE JAFFE JERRY MACKLEY COUNTY ADMiNLSTATTVE OFFICER HARRY M MAYS ADMINISTRATOR, ENVIRONMENTAL PUBLJC WORKS AGENCY B.L. INGRAM • • Paul F. Ryan, RS., MP.P.A., Director Stuart Long, Division Chief, Environmental Health Protection Service Peter S. Brierty, Division Chief, Haz Mat Mgmt sad Emer. Response Pamela Bennett, Acting Division Chief, Community Health Protection Sandra Alarcon-Lopez, Planning Consultant Gloria Anderson, Public Participation Coordinator Judy Orttung, Supervising Environmental Specialist Marilyn Kraft, Environmental Health Technician III Catherine Richards, Environmental Health Technician III Tanya Althiaer, Secretary I Arlene O. Payaa, Secretary 1 Gigi DePasquele, Clerk III Sharon Hightower, Planning Officer Steve Wilson, Division Chief, Policy Planning Division Michael O'Neill, Senior Planner, General Plan Team Julie Hemphill, Senior Planner, General Plan Team Ron Matyas, Associate Planner Brent Ellerbe, Computer Mapping Technician II • Michael Lerch, Senior Planner, Environmental Analysis Paul Kielhold, Assistant Planner, Environmental Analysis Marlyn Taub, Supervising Ilittstrator Victor Contreras, Illustrator II Joe Ainsworth, Illustrator I Karen Maher, Illustrator Trainee j~EPARTMENT OF SOLID WASTE MANAGEMENT Kea Jeske, Chief, Recycling and Panning Division Craig Gooch, Geographic Information Management System Manager Brent Rolf, Project Coordinator OFFICE OF MwNAGE>yIENT SERVICFc Wallace Raynor, Systems Development OMS Team Leader Rick Pourroy, Programmer IIJ r 1 U • wCKNOWLEDGMENT'S We w~onld like to ezpress onr sincere appreciation to the many individuals and organizations that devoted their time and ezpertise to the preparation of this plan. In partiwlar eve w~oald like to czprest onr tratitnde to the CHWMP Advisory Committee for their valuable input and eztraordinary commitment to the preparation of this plan. COUNTY HAZARDOUS WASTE MANAGEMENT PLAN • r~ U ADVISORY COMMf7"I'EE PEGGY SARTOR, CHAIR JOAN DOTSON, VICE CHAIR CHARLES BUQUET CHRISTINA FERRANTE PHIL GENTILE, JR. MICHAEL F. HAYWARD TOM IRWIN ARDYCE KOOBS JIM MULVIHILL JANET M. WEDER ~ __ i • • SAN BERNARDINO COUNTY HAZARDOUS WASTE MANAGEMENT PLAN TABLE OF CONTENTS INTRODUCTION 1.1 Introduction 1-1 1.2 Lcga1 Context I-2 1.3 The County Hazardous Waste Management Plan l-4 1.4 Goals and Policies/Actions 1-5 2. EXLSTING PROGRAMS FOR DEALING WITH HAZARDOUS MATERIALS AND HAZARDOUS WASTE 2.1 lntroductioa 2.1 • 2.2 Environmental Health Services 2-I 2.3 Fire Prevention Agencies 2-6 2.4 Agricultural Commissioner 2-6 2.5 County Land Management Department or Applicable City Planning Department 2-6 2.6 Solid Waste Management Department 2-6 2.7 Public Health Department 2-6 2.8 Other County Departmenu 2-7 2.9 Other Involved Agencies 2-7 3. WASTE GENERATION LEVELS, FACILITY WVENTORY AND NEEDS ASSESSMENT 3.1 Introduction 3-l 3.2 Data Uncertainties 3-3 3.3 Uncertainties in the Projections 3-6 3.4 Data Presentations 3-6 3.5 Discuuioa•and Analysis oC Data 3-103 3.6 Needs Assessment 3-105 3.7 Goals and Policies/Actions 3-108 4. WASTE MITIIMIZATTON 4.1 Introduction 4-1 • 4.2 Regulatory Requirements 4-1 4.3 Barriers to Waste Reduction 4-2 5. 6. a. 4.4 Incentives for Waste Minimization 4-3 4.5 State Waste Reduction Programs 4-3 4-6 County Waste Minimization Program 4-4 4-7 Generator Survey 4-S 4-8 Expansion of the County Program 4-7 4-9 Waste Reduction Goal 4.7 4-10 Goals and Policies/Actions 4.g SI'I'IIdG SPECIFIED HAZARDOUS WASTE FACB.ITIFS S.1 Introduction S.1 5.2 Description of 5peeified Hazardous Waste Facilities S-2 S.3 Local Siting Process to Comply with the Tanner Act S_g S.4 Goals and Policies/Actions 5-20 S.S Siting Criteria 5-28 GENERAL REQLTIRF.IdENT'S FOR HANDLING AND STORAGE OF HAZARDOUS MATERIALS 6.1 latrodnction ~ 6-1 6.2 Disclosure Requirements 6-1 6.3 Notification of Upset 6-2 6.4 Underground Storage Requirements 6-3 6.S Aboveground Storage Requirements 6-S 6.6 Home Occupation Permiu _ 6-S 6.7 Goals and Policies/Actions 6.S REGULATORY PROGRAM FOR GENERATORS (Including Transporters and new TSD faeilitiea) 7.1 Introduction 7.1 7.2 Identification of Hazardous Waste Generators 7-1 7.3 Busineu Licenses 7.2 7.4 Educational Assistance 7.2 7.5 Limited Quantity Generators 7-3 7.6 Disposal Auistance 7.3 7.7 Goals and Policies/Actions 7-4 LAND USE REQUIREMENTS FOR HAZARDOUS WASTE GENERATORS AND HAZARDOUS MATERIALS HANDLERS 8.1 Introduction a-1 2 • ~~ • _i • Pate Number 8.2 Land Use Requirements 8-1 8.3 Goals and Policies/Actions 8-S 9. HOUSEHOLD HAZARDOUS WASTE 9.1 Introduction g.l 9.2 Existing Program for Collection 9-1 9.3 Program Expansion 9-7 9.4 Goals and Policies/Actions 9-9 10. TRANSPORTATION 10.1 Introduction 10.1 10.2 Transportation Regulations L0.1 10.3 The Local Role 10.3 10.4 Rail Transport and the Need for a Comprehensive Study 10.'I 10.5 Goals and Policies/ACtioas 10.8 11. ENFORCEMENT AND EMERGENCY RESPONSE • 11.] Introduction 11.1 11.2 Enforeemeat 11-1 11.3 Emergency Response 11.2 11.4 Goals aad Policies/Actions 11-4 12. SITE MITIGATION AND LONG TERM REMEDIAL ACTION 12.1 Introduction 12-1 12.2 Identification of Sites 12-1 12.3 Oversight at Cleanup !2-S 12.4 Development/Land Usc Applications at Listed Sites 12-6 12.5 Coordination of Assessment and Cleanup at Solid Wsste Sites 12-6 12.6 Goals and Policies/Actions 12-6 13. PUBLIC EDUCATION AND PARTICIPATION 13.1 Introduction 13-1 13.2 Program Compoaenu 13-1 13.3 On-going Public Education/Public • Participation 13-4 13.4 Goals and Policies/Actions 13-9 3 r~ LJ $ee Nnmher la. n~L>~NrwnoN scl~DULE wND ORGANIZATIONAL RESPONSIBILITIFS 14.1 Introduction 14-! 142 Organizational Responsibilities l4-1 14.3 The Implementation of Polices/Actions 14-4 14.4 Implementation Scbednles 14.E APPENDICES A) Glossary B) Legislation regarding Haurdous Wastes C) Regional Planning Documents D) Waste Codes, Wastc Groups, and Generalized Treatment Methods E) Justification for the Saa Bernardino County Siting Criteria F) General Designation Maps G) State Expenditure Plan H) Public Education and Participation I) Hazardons Materials/Wastes Directory J) Comments received oa the Draft CHWMP sad response to Comments • (A separate document) K. Fair Share Language L. M.O.U. with B.L.M. regarding siting of hazardous waste facilities. • ri ~r 4 ~~ 1.1 INTRODUCTION CHAPTER] INTRODUCTION r~ Proper hazardous waste management constitutes one of the state's major environmental concerns. Statewide recognition of the aced for better methods of hazardous waste management came about by the intense media attention on improper disDOSaI practices. Hazardous chemicals play an important role in our modern society. They contribute to the manufacture oC a vast array oC consumer products (i.c„ televisions, computers, automobiles, and medicines) and the convenience of consumer services (i.e„ dry cleaners, automotive repair). While these goods and services add to our quality of life, they also cause the generation of hazardous waste. Reducing our reliance on hazardous materials would reduce the generation of waste. Hazardous waste will continue to be generated, however, since some materials have no substitutes. For this reason, a comprehensive plan is necettary to identify and promote programs Cor the reduction oC hazardous waste and the safe management oC wastes that remain after treatment or recycling. Hazardous waste is defined in the California Health and Safety Code, • Section 25117, as consisting oC " a waste or combination of waste which because of its quantity, concentration, or physical, chemical or infectious characteristics, may either. • Cause, or significantly contribute to an iaercase in mortality or an increase in serious irreversible, or incapacitating reversible illness, or • Pose a substantial present or potential hazard to human health or environment when improperly treated, stored, transported or disposed of or otherwise managed.' San Bernardino County generates about 65,000 tons of hazardous waste Der year. The County's waste stream represents about 5% of the wastes generated in the Southern California region. The major categories of waste produced in the County include metal containing liquids, waste oil, oily sludges, and baghouse waste. These wastes come from a variety of industries ranging from small businesses, such as automotive services and plating companies, to large industries like steel manufacturing. In order to manage the wastes generated in the County a thorough analysis of the situation is required. The County Haurdous Waste Management Plan (CHWMP) provides a comprehensive ducuuion of the amounts and types of wastes generated, programs to reduce the amount of waste generated, the County's need for specified hazardous waste facilitiu, and identifies goals and policies regarding the management oC hazardous • wastes. The CHWMP supersedes the Hazardous Waste Management chapter of the Solid Waste Management Plan. Although this Pian focuses on haurdous waste management, hazardous materials management is also addressed. Haurdous materials are uuble subsunces whereas hazardous wastes are subsunces oC no Curtner intended use that require treatment or disposal. Some iuue areas (ie. transporution, storage, and emergency ruponu) require an analysis of both hazardous material sad waste because issues or programs related to rhea two substances overlap. The inclusion of information regarding haurdous materials also meets this jurisdiction's concern for a comprehensive management plan. Whenever possible, the diacnssion of hazardous materials and haurdous wastes is separated in order to comply with our obligation under the enabling legislation to focus oa haurdous waste management. 1.2 LEGAL CONTEXT Federal and state laws mandate an improvement in the management of hazardous waste. These laws demand that gcnerators take more responsibility Cor the w:arcs they generate and require certain actions be implemented to reduce the amount oC wastes being generated. Past practices of burying untreated hazardous waste in landfills are being phased out, and generators must implement alternative technologies that reduce the toxicity and volume of wastes. The critical date in federal and state law is May 8, 1990 after which all land dispoul of untruted hazardous waste is banned. (The exception to the ban is Cor special • wastes and solid wastes generated from cleanup of a haurdous waste site.) AB 2948 (Chapter 1504, Sutures of 1986) and amending legislation SB 477 (Chapter 1167, Sutures of 1987), AB 3206 (Chapter 1389, Sututea oC 1988), - AB 3209 (Chapter 378, Sutntes of 1988), and AB 34 (pending), recognized the need to have a comprehensive program Cor management of wastes by authorizing counties to develop a local haurdous wastc management plan. (The legislation is presented in Appendix B.) The Iaw has as its goals: - the safe and responsible management of haurdous waste; - the effective siting of hazardous waste facilities that involves local and sate governments, the public, and private industry; sad - the prevention of permanent haurdous waste disposal into the land or emission in the air without first processing the waste by an economically and technically feasible alternative technology. State Iaw specifies the requiremenu for the adoption and approval of the Plan sad identifies eight accessary elements. These eight elemenu include: 1) Aa analysis of the volume and type of haurdous wastes generated in the County sad estimates of the expected rates of production by type of waste to the year 1994. 2) A description of the existing specified haurdous waste facilities • within the County including a determination of existing capacity. 1-2 '. _ C~ • 3) An analysis of the potential Cor waste reduction sad recycling in the County. 4) A consideration of the need to manage the small volumes oC hazardous wastc produced by busineues and households. 5) A determination oC the aced for additional specified haurdous waste facilities to manage the volumes of haurdous waste currently generated or the volumes projected to be generated is the near future. 6) A set of. criteria for siting new or expanded specified hazardous waste facilities and the daigaation oC general areas where the criteria might apply. 7) A statement of goals, objectives, and policies for the siting of hazardous waste facilities and the general management oC hazardous wastes through the year 2000. 8) A schedule for the implementation measures identified in the Plan. The CHWMP preparation sad adoption must include an extensive pubIie participation effort. State law mandates the establishment of a committee to advise County staff and local government officials on issues pertaining to management of hazardous routes. The advisory committee holds informal public meetings and workshops to provide public information as • well as take public comment. The committee must consist oC at lent seven members and include a representative from industry, a representative from an environmental organiution, and a representative from the general public. These members are appointed by the County Board of Supervisors. The Board may appoint other members who have expertise in the field of hazardous waste management. At least three members must be city representatives appointed by the City Selection Committee. 1.2.1 Plan Adoption and Amendment A final copy of the CHWMP must be submitted to the California Department of Health Services (DHS) by June 1, 1989. State law specifies that the CHWMP must be approved by a majority of the cities within the County which contain a majority of the population of the incorporated area of the County. Once the Pian has been approved by DHS, the County has 180 days from the date the DHS approves the CHWMP to incorporate applicable portions of the Plan by reference into the County's general plan, or enact an ordinance requiring all applicable zoning, subdivision, conditional use permit, and variance decisions to be consistent. with the CHWMP. The cities are also required by state law to adopt some Corm of a Haurdous Waste Management Plan. The taw specifies that cities are required to do one oC the following: I) adopt a City Haurdous Waste Management Plan which is consistent with the CHWMP; 2) incorporate • applicable portions of the CHWMP into the city's general plan, or 3) enact an ordinance which requires that all applicable zoning, subdivision, 1-3 ~ ~ ~J conditional use permit, and variance decisions to be consistent with the applicable portions of the CHWMP. State law does not limit the city's authority to attach conditions to the iuuanee of t land use application or to establish requirements or siting criteria different from those identified in the CHWMP. Any such conditions or criteria established by a city . must be subsuntiated as necessary to protect the public health and ufety since the conditions or criteria may be appealed to the State Appeal Board (SB 477, Chapter 1167, Statutes of 1987). The Guidelines for Preparation oC Hazardous Waste Management Plans recommends that the CHWMP be updated once every three years. This refers only to a complete revision oC the Plan. Aay amendment to the CHWMP must be approved by the DHS, the County, and a majority of the cities containing a majority of the population is the County. 13 THE COUNTY HAZARDOUS WASTE MANAGEMENT PLAN On March 31, 1987 the County of San Bernardino Board oC Supervisors authorized the preparation of the CHWMP. A resolution was adopted and sent to the Statc Department of Health Services specifying the County's desire .to prepare the CHWMP. The Plan is consistent with state law and the Guidelines for Preparation of Haurdous Waste Management Plans prepared by the Department of Health Services, lone 1987. The CHWMP serves as the primary planning document for the management • of haurdous waste in San Bernardino County. It is an element of the County's General Plaa and is consistent with other elements of the ~ General Plan. The CHWMP identifies the types and amounts oC wutes generated in the County, establishes programs for managing these wastes, identifies an application review process Cor the siting of specified hazardous waste facilities, identifies mechanisms for reducing the amount of waste generated in the County, and identifies goals and poIieies and actions for hazardous waste management. The CHWMP was prepared with Cull and meaningful involvement of the public. Information regarding the County's CHWMP Advisory Committee and public involvement efforts is presented in the discussion on public participation, Chapter 13. Development of the CHWMP was a difficult task because of continuous changes is legislation sad the resultant changes in technological requirements. Legislation has changed during the last several years and continues to change dramatically u a result of public awareness regarding the problems sad issues associated with effective hazardous waste management. .Due to rapidly changing requirements, increasing fees and taxes, and uncertain future liability, many generators are changing their management practices in order to minimiu their generation oC hazardous waste. Additionally, the technology available for waste reduction sad on- site treatment is also changing rapidly as a result of recent legislation. Despite legislative changes, consistent sad sccurafe data do not exist on current levels of waste generation and management practices. Thus, the • CHWMP sot only identifies a.set of goals sad policies for a comprehensive hazardous waste management program, but also identifies the limitations of the data and resources. . j; 1-4 • 13.I Department of Environmental Health Services The San Bernardino County Department of Environmental Health Services (DEHS) is the primary agency responsible for preparing the CHWMP. The DEHS administer several programs that promote effective management of hazardous materials and waste management, as well ss permiu and regulates hazardous waste generator in the County. Ia 1983, the DEHS signed a Memorandum of Understanding (MOU) with the State Department of Health Services authorizing DEHS to enforce the haurdous waste control taws of the State. The MOU and state taw provide that DEHS enforce hazardous waste regulations in the incorporated cities as well as the unincorporated areas of the County. 132 Complianx with the California Environmental QnaIity Aet The preparation of the CHWMP falls under the definition of a project as defined in the California Environmental Quality Act (CEQA), Public Resources Code, Section 21000 et. seq_ Aa initial study identified-the potential for several significant environmental impacts, and thus an Environmental Impact Report wee prepared and reviewed in accordance with CEQA requirements prior to Plan adoption. 133 Regional Hsssrdons Waste Management • San Bernardino County is a member oC the Southern California Hazardous Waste Management Authority (Authority). Other member jurisdictions include the County of Santa Barbara, County of Ventura, County of Riverside, County of Orange, County of Imperial, County of Ssn Diego, City of Los Angeles, and the cities within the counties. The Authority coordinates the implementation of the Action Program that ensures the development of programs and the siting of hazardous waste facilities sufficient to safely manage hazardous wastes generated within Southern California. The Authority was formed in 1985 under a Joint Powers Agreement. This Agreement was based on the 'fair share' concept which states that. "every city and county is the region will accept responsibility for the management of hazardous wastes in an amount proportional to the hazardous waste generated within the city or county.' The Authority agreement and the 'fair share' principles are found in Appendix C. The County, through its membership in the Authority, participates in the preparation of the Regional Hazardous Waste Management Plan. The Regional Plan serves as a rtsource document that identifies haurdous waste management issues, needs, and solutions at the regional level. The regional plea includes a fair share formula and regional action plan developed to implement the regional plan (See Appendix C). In addition, a state-wide plan will also be prepared by the Department of Health Services in 1989. 1.4 GOALS AND POLICIES/ACTIONS • The County plan is intended to preserve the local land use process, protect the local environment, and provide a framework Cor ensuring that 1-S needed facilities are sited..The following overall goals and policies/actions are the underlying goals used to develop the CHWMP. 1.4.1 Goals G-1•I To protect the health and welfare of the public, environment, and economy oC San Bernardino County through a comprehensive program that ensures Cafe and responsible management oC hazardous. waste/material. . G-1-2' To reduce the amount of hazardous waste generated is the County by providing improved programs for haardous waste source reduction and recycling. G-1-3 To ensure proper management of hazardous waste/material by identifying and encouraging safe and .efficient methods for managing hazardous waste/material and by providing for needed hazardous waste facilities in San Bernardino County. G-1-4 To prevent hazardous waste Crom being permanently disposed into land, or emitted into the air without being processed by as economically and technically feasible alternative technology. G-1-5 To involve the public, industry, and government is a comprehensive process that develops solutions for the management and disposal of h:zardous waste. G-I-6 To establish a framework for the development of San Bernardino County's share of hazardous waste facilities G-1.7 To recognize that coasnmers contribute to the generation oC hazardous waste, thus, limiting industrial growth is not an appropriate means of reducing the County's commitment is hazardous wastc management. G-1-8 To encourage and develop public education programs on the proper management and disposal of hazardous waste. 1.42 Policies/Actions P/A-1-1 Because a aced exists to augment current programs Cor the proper management of hazardous waste and to address recent legislation, this jurisdiction :hall work with industry and the public is identifying safe and responsible solutions for the management and disposal of hazardous wastes P/A-1-2 Because the CHWMP applies County-wide, the County and the cities shall work together to prepare and update the Cliwh~ as well as its implementing ordinances and to develop and implement programs which reduce the amount and toxicity oC the haurdous waste generated in the County. I-6 ;: • is • P/A-1-3 Because the Southern California Hazardous Waste Management Authority (Authority) provides to appropriate forum for local input regarding the regional Citing of haurdous waste facilities, this jurisdiction shall continue its participation is the Authority. P/A-1-4 Because proper haurdous waste management is one of the state's critical environmenul concerns, the County and the cities shall work with the Authority sad the state to addreu regional and statewide planning issues as necesury to achieve environmentally and economically effective haurdous route management on a local, regional, sad statewide basis. • 1-7 CHAPTER 2 EXLSTING PROGRAMS FOR DEALING WITH HAZARDOUS MATERIALS AND HAZARDOUS WASTES 21 INTRODUCTION The County of San Bernardino's extensive experience with hazardous material/waste issues resulu from a long standing involvement (since 1981) in the development of programs that address hazardous material and waste management problems. Innovative and comprehensive programs have been developed to address the proper management of household hazardous waste, to respond to emergency situations in a comprehensive, organized manner, and to provide regulatory information and assistance to industry. These programs have served as models for other jurisdictions concerned with similar issues. Although, such programs have gained the county widespread recognition in the field, additional efforu are accessary to encourage and assist industry with waste minimization efforu and to augment the current data system on hazardous waste generators. • The County has several departmenu involved in hazardous material/waste programs: the Environmental Health Services Department, the Fire Department, the Land Management Department, the County Agricultural .Commissioner, the Sotid Waste Management Department, the Public Health Department, the Sheriffs OfCiee, and the District Attorney. OC these departmenu, the Environmental Health Services Department has responsibility Cor the majority oC Drograms which deal with hazardous material and waste issues. Other agencies involved in hazardous materials and wastes include: the South Coast Air Quality Management District, the Regional Water Quality Control Board, and Publicly Owned Treatment Works. The discussion below identifies the programs administered by the different County Departments and other agencies. It is intended as a background to the policies and programs discussed throughout the CHWMP. State and federal roles are discussed throughout the plan and summarized in Chapter 14. 22 ENVIRONMENTAL HEALTH SERVICES The Department of Environmental Health Services (DEHS) has earned national recognition for their expertise in the field oC hazardous material/waste management and their innovative development of specialised programs. Many of the professional staff have seven or more years of experience, a significant achievement given the newness of the field. Professional staff have a wide range oC skills with advanced degrees in • the following area: public health. environmental health, biology, chemistry, geology, and other related sciences. Because oC the Department's expertise, 2-1 r~ LJ DENS staff have helped to conduct training aeuions sponsored by the California Conference of Directors of Environmental Health for sew employees. Other noteworthy efforu have included teaching courses in the University of California Hazardous Materials Certificate program, presenting one-time lectures for the Certificate Program, and, for the past three years, participating in the National Conference on Household Hazardous Waste. The DEHS is the most involved Department in regulating hazardous waste and material management in the County. The DEHS is responsible for the following work areas: • Hazardous waste, infectious waste, tonic substances; • Liquid and solid waste sanitation, refuse disposal, litter control; • Air Quality control; • Water supply and water quality; • Food and milk protection; Insect and rodent vector control; • Sanitation of public swimming pools and public bathing areas; • Maintenance, ventilation, and sanitation of housing and institutions; housing rehabilitation and mobilehome installations; • Land use enforcement, noise control; and • Nuisance abatement The DEHS contracts services to the cities within the County, thus, DEHS • implements these programs county-wide. The DEHS carries out :event hazardous material/waste management programs. There programs ~ are 1 summarized below. 2.2.1 Hazardous Materials Management sad Emergency Response Division The Hazardous Materials Management and Emergency Response Division of the DEHS enforces many of the provisions oC the Resource Conservation and Recovery Act (RCRA), the CaIiforais Hazardous Waste Control Aet, and Title 22 of the California Code of Regulations. It bas eight major programs that addreu the requirements of state and federal legislation. The programs include the Generator Permit Program, the Underground Storage Tank Program, the Hazardous Material Handler Program, the Household Hazardous Waste Collection Program, Site Remediation Program, Infectious Waste Program, Radiological Health Program, and the Program for the preparation of the County Hazardous Waste Management Plan. The DEHS allocates 36 professional staff positions for the implementation of these programs. Generator Permit Prearam The Hazardous Waste Generator Program monitors all busineues that generate or produce hazardous waste Cor. complianet: with state laws sad • regulations. Haurdous waste geaenton are required to have a permit from the DEHS. The Program consisu of three major components 2-2 M ~J • - A regulatory component to verify compliance with state and federal regulations. The program includes inspection, monitoring, and the permitting oC hazardous waste generators. - An enforcement component to ensure violations are corrected. Enforcement of regulations is coordinated with the State Department of Health Services, and other local, regional, and state agencies involved is haurdous waste management. - An educational component that consisu of providing haurdous waste generators with information regarding proper management of hazardous waste as well as resources and methods for waste reduction and recycling. The Uaderground Storage Tank Program is a requirement of RCRA (Subtitle C) and the California Health and Safety Code (Section 25280 - 25299.6). Existing laws require that all underground haurdous materials storage tanks be registered with the State Water Resources Control Board and that the owners of these teaks receive a permit to operate from the local enforcement agency (DEHS). The DEHS regulates all tanks, monitors the installation of new tanks, and ensures continued compliance with regulations through a annual inspection of facilities. (Fora discussion of above ground storage, see Chapter 6.) • Hazardous Material Handler Program The Hazardous Materials Handier Program admiaisters the State requirements for a Business Plan (AB 2185, Chapter 1167, Statutes of 1986 and AB 2187, Chapter 463, Statutes of 1986) and a Risk Management Prevention Program (AB 3777, Chapter 1260, Statutes of 1986). State law requires that information be made available to the public, government officials, and emergency response personnel regarding the location, type, approximate quantity, and health risk of hazardous materials and wsste stored at business facilities. DEHS receives and reviews business plans from industry and distributes approved plans to other emergency responders. As required by state law, the County has developed a County-wide Emergency Response Area Plaa based on information from individual business plans. In addition, the program includes permitting of hazardons material handlers who store haurdous waste onsite. DENS is respoasible for verification of the chemical inventory reported in the business plan. E~esehold Hazardous Waste Collection Program The county sponsors five household haurdous waste collection center; the centers are located in San Bernardino, Redlands, Vietorville, Bartow, and Rancho Cucamonga. Funding for this program is baud on a surcharge on solid waste disposed at county landfills (currently S25 Der ton). The collection ceaters are operated by city or county employees; the DEHS • provides technical support and oversight to theae centers. Additionally, the Department sponsors one day collection Drograms is areas oC the 2-3 + ~ • County not currently served by a collection tearer. In 1987 the DENS • carried out nine 'Household Hazardous Waste Round-ups' throughout the incorporated sad unincorporated areas of the County. (See Chapter 9 for more information about the prognm.) The site remediation prognm oversees the clean-up of spills and accidental releases of hsurdous materials. Currently, the prognm focuses on spills resulting from leaking underground storage oaks. In addition prognm staff works with other programs in the Department to assist in comprehensive groundwater and soils investigation. Infectious Waste Program The program regulates the storage, handling, and disposal of infectious wastes by large industry. It includes inspection and permitting oC facilities generating infectious waste. The program may be expanded to include small businesses since improper management of infectious waste by these businesses also Dose a danger to public health and the environment The DEHS's Radiological Health Program focuses on three major areas. The fiat includes the inspection of x-ray machines in San Bernardino • County wader contract with the State. The purpose of the prognm is to inspect x-ray machines Cor compliance with state taw and to reduce radiation exposure to patients and to workers. The second area consists of planning for the safe operation of Ca[iforaia's first tow-level radioactive waste disposal site. Acting as the County's lead agency, the DEHS hopes to prevent or safely manage any radiation hazards by successfully planning and coordinating with other county, state, sad federal agencies. The final area incorporates the management oC all other ionizing radiation issues. For example, DEHS has an information program for radon gas and provides emergency response to any radiological incident The DEHS is also responsible for the preparation and implementation oC the Hazardous Waste Management Plan authorized wader AB 2948. The preparation of the Plaa has included extensive public involvement, data manipulation and analysis, and the development of goals and polities Cor the effective management of hazardous waste in the County. The Plan also provides a comprehensive discussion of the local permit process required for the siting of specified hazardous waste facilities in this County. 2-4 . 2.22 Emersenry Response Emergency Services is a separate section within the DEHS. This section coordinates emergency response activities, procures training programs for first responders, and prepares and updates emergency response plans. Emergency Services has had sa active emergency response program for the past seven years. In 19g1, an emergency response team was established and the County's fiat emergency response plan was developed. The plan became a model used by other local and state agencies to develop similar emergency response programs. 223 Air Pollution Control District The Air Pollution Control District (APCD), a separate division in DEHS, is responsible for regulating and monitoring the air emissions Crom industry, including specified hazardous waste facilities. The APCD acts pursuant to the federal Clean Air Act, the California Health and Safety Code (Section 41700), and the APCD Rules and Regulations. The APCD has jurisdiction over the desert areas. The mountain and valley areas oC the County are regulated through the South Coast Air Quality Management District 22.4 Other Closely Related DEHS Programs - The DEHS administers several other programs which deserve mention. These programs include Water Hygiene, Waste Management, and Land Use • Control and Noise control. Water Hv¢iene The DEHS ensures that water system facilities are properly operated and designed. The DEHS permits water well construction and enforces water quality standards through the State Safe Drinking Water Act. The DEHS also 'provides technical support regarding watei quality issues for ell development projects proposed in the County. Waste Management The DEHS has an extensive solid waste management program and serves as the Cities and County local enforcement agency for wastes. The program consists of long range planning, enforcement of state and local collection, storage, transfer, and disposal requiremenu, Litter control, resource recovery and recycling, and liquid waste management. The DEHS provides consultation, resource planning, and input on environmental and public health issues for all land use activities including CEQA review, long range planning, and the land use permit process. The DEHS provides technical support on issues aueh as evaluation of public health impacts, prevention of groundwater contamination, availability of • water supplies for new developments, and compliance with environmental and public health laws and regulations. The DEHS also issues Special Uae 2-S Permits (SUP). The SUP is usually required to ensure that a development • is monitored and operated according to the conditions of approval for the land use permit 23 FIRE PREVENTION AGENCIES The City Fire Department, County Forestry wad Fire Warden Department, wad Fire Districts are involved in the management of hazardous material/waste. The Fire Agencies are one oC several key ageneiea in the Interagency Emergency Response Team. They serve as scene manager Cor off-highway emergency situations and are responsible Cor ensuring the safety of the public. The Fire Agencies are often involved in overseeing the removal of underground storage tanks along with other agencies tuck as DEHS. In addition, some Fire Agencies operate household collection centers. 24 AGRICULTURAL COMMLSSIONER The Agricultural Commissioner regulates Dcsticide use under the provisions of the California Food and Agricultural Code, the California Code of Regulations, the Government Code, and local ordinances. These laws provide for the proper use oC pesticides and the protection of consumers and workers who might be exposed to pesticides. The Agricultural Commissioner's Office also operates a Household Hazardous Waste Collection program. • 25 COUNTY LAND MANAGEMENT DEPARTMENT OR CITY PLANNING DEPARTMENT The County Laad Management Department is responsible for the issuance oC land use permits for development in the nnineorporated arcs of the County, and, thus, is responsible for the environmental review and permitting of specified hazardous waste facilities within iu jurisdiction. In City jurisdiction, the City Planning Department is responsible for the environmental evaluation of facility applications and the permitting of specified hazardous waste facilities. 26 SOLID WASTE MANAGEMENT DEPARTMENT The Solid Waste Management Department is responsible for management of municipal waste facilities wad Cor monitoring the types of waste disposed at these facilities. Proposals are included in the Solid Waste Management Plan for the operation of household hazardous waste collection facilities at these sites. 27 PUBLIC HEALTH DEPARTMENT The Public Health Department has responsibility for epidemiological studies and activities including those relating to hazardous substance exposures • which may effect the general public health. The Health Office is the lead agent for public health emergencies and as the lead agent provides 2-6 . -- • i • oversight of the medical emergency delivery systems. , 2E OTHER COUN'T'Y DEPARTMENTS The County Sheriffs Office and Law enforcement Agencies participate on the emcrgeacy response team. Law enforcement agencies ensure site security, provide crowd and tnffic control, and take all feasible actions to protect life in the event of a hazardous material/waste emcrgeacy. The County Sheriff a Office coordinates all responding agencies and evaluates the severity of the emergency situation. The District Attorney (DA) provides legal support for violations of hazardous materials and hazardous waste management violations. The DA and the County Sheriff's Office participate on the Strike Force. The strike force coordinates the investigation of major hazardous waste violations, evaluates the severity of the violation, and determines the appropriate course of action. 29 OTHER INVOLVED AGENCIES 29.1 Publicly Owned Treatment Works Publicly Owned Treatment works set discharge levels for local industry discharge oC waste water. • 29.2 Sonth Coast Air QnaIity Management District (SCAQMD) The SCAQMD is responsible for regulating and monitoring air emissions from industry, including specified hazardous waste facilities. The SCAQMD acts pursuant to the federal Clean Air Act, the GliCornia Health and Safety Code (Section 41700), and the SCAQMD rules and regulations. The SCAQMD has jurisdiction over the mountain and valley areas. The desert areas are regulated through the Air Pollution Control District. 29.3 Regional Water Qaality Control Board (RWQCB) The RWQCB issues water discharge permits, monitors water quality, and can take enforcement actions against violators. The RWQCB is responsible Cor the control of water pollution. • 2-7 ~ i ~ CHAPTER s WASTE GENERATION LE~rElS, FACILITY INVENTOIl:Y, AND NEEDS ASSESSMENT 3.1 IIr"TRODUCT'ION Comprehensive and accurate data on hazardous waste generation levels and man- agement practices are critical elements of a Haznrdous Waste Management Plan. A clear understanding of current waste generation and management practices provides the basis for identifying program and facility needs. Comprehensive data provide a quantitative understanding of what types and amounts of hazardous waste are gen- erated; by whom; why; and how it is treated and/or disposed. Analysis of the data will identify opportunities for waste minimization. FCnowledge of waste generation levels and management practices also serve as the basis for developing or fine tuning regulatory compliance programs, as well as eduentional and technical assistance pro- grams. This information identifies areas to emphasize in the training of regulatory compliance inspectors and emergency responders. Finally, current and projected waste generation levelc, when coupled with data regarding treatment capacity, should identify facility needs. Despite the critics] importance of accurate and comprehensive data to support policy direction, program development, and identify facility needs, however, serious efforts • to track this information and analyze it have been undertaken only recently. Al- though there have been several efforts at the national levell to quantify waste gener- ation levels and identify the number of generators, recent legislation (AB 2948, Chapter 1504, Statutes of 1986) authorized the first statewide program in California This program provided for the preparation of County Hazardous Waste Management Plans which include the analysis and interpretation of local data. Perhaps the most important benefit of this statewide program is that each county will assess its needs and develop polities and procedures for addressing them. Because this is the first systematic effort in data collection and analysis, several significant concerns with the data have been encountered. As a result, this chapter recommends a County data collection and management program. The primary source of the data presented in this chapter is the California Depar4 ment of Health Services (DHS) Hazardous Waste Information System (HRrIS). The HWIS tracks all manifested shipments of hazardous waste in California. Data regarding hazardous waste shipments into and out of San Bernardino County during 1986 and 1987 were provided to the County Department of Environmental Health Services (DEHS) on a magnetic tape. This data was analyzed and supplemented with information from DEHS files, Biennial Reports (as available), and telephone in- terviews with individual generators, transporters and facilities (as necessary). The data are presented in s series of Tables, A - Q, which were developed in aaor• dance with the methodology called for in the California Department of Health Ser- vices' Guidelines for the Preneration of Hazardous Waste Management Plane. These Tables att presented in the format and order called for m the Gutdeltnea Tables A - • J analyze the 1986 and 1987 data. Tables S - Q project waste generation levels to the year 2000. A listing of the Tables is provided on the next page. 1 Rcvicwcd in State of the Environment A View toward the Nineties, A Repon from The Con- scrwrtion Foundation, Washingtott D.C., 1987. 3-1 i ~ r LIST OF DATA TABLES Table A Quantities of hazardous waste shipped offsite in 1966 and 1987 by Generatorain San Bernardino County Table B Current county needs assessment for commercial hazardous waste treatment/disposal eapasty Table C Commerdal hazardous waste treatment facilities in San Bernar- dino County Table D Current county Heads easessment for commercial hazardous waste treatmentldisposal capacity Tab]e E Quantities of hazardous waste imported into San Bernardino County 1986 and 1987 Table F Quantities of hazardous waste exported from San Bernardino County, 1986 and 1987 Table G Commerdal hazardous waste storage capacity and activity Table H-1 On-site treatmentldisposal of hazardous waste in San Bernardino County - 1986 total, all facilities Table H-2 On-site treatment/disposal of hazardous waste in San Bernardino County, 1986, by facility Table I Multi year planning estimate of quantities of hazardous waste shipped offsite Table J Industrial sources of hazardous wastes Table R Projected quantities of hazardous waste generated by major indus- try groups (2000) Table L Projected quantities of clean up activity waste Table M Projected quantities of new hazardous waste streams Table N-1 Total projected quantities of hazardous waste shipped offsite in 2000 (No waste minimization) Table N•2 Tots] projected quantities of hazardous waste shipped offsite in 2000 (With waste minimization) Table 0 Projected commercial hazardous waste treatment and disposal Ca- padty in San Bernardino County Table P-1 Projected needs assessment for commercial hazardous waste treat- ment eapadty (No waste minimization) Table P-2 Projected needs assessment for commercial hazardous waste treat- ment capadty (With waste minimization) Table Q-1 Projected quantity of residuals generation (No waste minimiza- tion) Table Q-2 Projected quantity of residuals generation (With waste minimiza- tion) • 3.2 • 32 DATA UNCERTAINITES As indicated above, several factors have been identified which lead to considerable uncertainty in the data. These faetore include the hazardous waste classification system, generators' hazardous waste management practices, and the Hazardous Waste Information System. A description of these factors, how each contributes to the uncertainty of the data and where feasible, efforts to correct for these un- certainties in this Plan follows. 32.1 Hazardous Waste Classification System A classification system which provides a unique identifying code for each type of waste is essential for tracking waste generation levels and management practices. California currently uses a three digit classification system developed at the Univer- sity of California, Davis which is based on the primary chemical characteristics of the waste. California's waste classification system is shown in Appendix D. (T'his classi- fication system is used only in the states of California and Washington. At the feder- al level, the Environmental Protection Agency has adopted a more complex system which takes into consideration both the chemical characteristics and the source of the waste.) Ideally, a classification system should provide a unique code for each type of waste and should be easily understood by hazardous waste generators. How- ever, since most wastes are often mixtures, rather than a single chemical component, it is possible that more than one code will be appropriate to describe a particular waste. Unfortunately, generators may use different codes to describe what is essen- • tially a similar waste. For example, some generators will use the waste code for con- taminated soil, while others choose to use the code specific to the chemical character- istic of the soil contamination. This problem is compounded by the feet that.as the regulations change, describing a waste in one manner may cause it to be subject to e landfill ban, whereas under some other waste code, it may still be accepted at a 1end- fill. This has caused some generators to use different waste codes to describe the same waste. These practices cause considerable uncertainty in the date and un- fortunately een not be easily corrected. Because of the complexity of the elassifice- tion system and its demand for user knowledge of the chemical characteristics of the waste, many hazardous waste generators have difficulty understanding and using the system. Consequently, many manifests are improperly filled out or not com- pleted. Recent regulatory changes now require that both the state and federal elassi- fieation codes be included on manifests, further compounding the generator's confu- sion and need for assistance. San Bernardino County Department of Environmental Health Services currently provides a variety of educational programs which assist hazardous waste generators in complying with the laws. While these programs will help considerably over the long term, it is not possible to correct existing data to remedy these problems. 322 Generator's Waste Management Practices Knowledge of generator's waste management praeticee is essential to analyzing and interpreting the waste generation data It should be noted that while there have been hazardous waste management laws in place in California since the early 1970's, they have not been enforced in the same way as now. The number of wastes categorised • as hazardous has changed as our understanding of the iuue has changed. Many more wastes are included now than when these laws were originally passed. Addi- tionally, the laws have only recently been enforced at the local level in those counties 3-3 r~ LJ with a Memorandum of Understanding (MOU) with the California Department of Health Services. The MOU has allowed local agencies to take on the responsibility for enforcing state hazardous waste control laws as they apply to generators. Con- sequently, amajor educational effort has been necessary to inform hazardous waste generators of their ob)igations under the law. Afnny generators have or had an accumulation of wastes on their property which they were storing or they did not know what to do-with the wastes. These generators are willing to comply once informed by a county inspector about how W properly manage their wastes. However, the wastes which are then manifested do not tru)y represent waste generated that yeu, but rather reflect an amount accumulated over some longer period of time. Using existing generation levels as a basis for ealeulab ing facility needs will thus overestimate the problem. While this will continue to be the ease until all generators are brought into the regulatory program, apparent ~•aste generation )evels should drop after that Another past management practice which greatly affects both the data and the ability to retyele and/or reuse these wastes is the tendency of many generators to mix ~•astes. For example, frequently employees at automotive repair shops have mixed waste solvents, crankcase oil and antifreeze. Not only does this reduce our ability to recycle these materials, it is difficult to assign an accurate waste code to such a mix• lure. Extensive educational efforts by regulatory agenoes and the ntyeling industry are helping to overcome Chic problem. However, until all small quantity generators are brought into the program, waste data will not accurately reflect wastes generated • or recycling opportunities. Again, these uncertainties in. the system care not be eor- reeted now, but should be reduced over time. The waste tracking system nationwide is based on the use of a site-apedfie unique identification number assigned to each hazardous waste generator. Generators with multiple sites should be assigned a dilfennt identification number for each cite. Un- fortunateiy, not el] generators understand the system. In the process of reviewing the data, Department of Environmental Health Services staff became aware of one instance in which a statewide company was using the identification number assigned to a county generator for all of its wastes. This practice was discovered by an effort to verify the large and diverse volume of waste coming from a seemingly small opere- tion. Those wastes generated outside of San Bernardino County wen deleted from the databases It is not known how common this practice is among generators. De- partment of Environmental Health Services staff made every effort to verify unuauel- )y large volumes or types of wastes. No other corrections were found to be neceuary. 32.3 Hazardous Waste Information System The primary soune for the data presented in this Plan is the California Department of Health Services Hazardous Waste Information (HWIS) System. This automated database tracks all hazardous wastes generated in California as recorded on manifests which are required to be sent to the Department by both the generator and the treatment or disposal facility. Uncertainties in the data an the result of the manner in which certain wastes are tracked in the Hazardous Waste Information System, converting measures of weight and volume to a standard unit, and errors in . entering manifest information. The HWIS rystem initially was set rap to track primarily wastes generated and treated or disposed of in California. Wastes shipped n out-of--state were not originally included. An effort to include outofatate shipments 3-4 • was begun in 1986 bui was not tromplete. As a result, the 1986 data underestimates actual waste generation levels. The California Department of Health Services did obtain some data on out-of--state shipments in 1986. This information was provided to the County and has been added to the 1986 figures. According to a representative of the California Department of Health Services, the 1987 HWIS data does include out-of--state shipments. Another source of uncertainty in the data is caused by the feet that in California, the State Department of Health Services grants a variance from the full manifesting re- quirements for hazardous waste haulers who transport each wastes as waste oils, dry cleaning solvents, and parts cleaners. This program is designed to promote recycling and to assist small businesses that generate any of the wastes listed above. The revised procedures allow the transporter to prepare the manifest and combine wastes from multiple generators. As a result, the transporter becomes the only "generaWr" of record in the HWIS data base. Because most route haul transporters operate in more than one county, the data base erroneously assigns all wastes handled by each company to the county where the transporter is based. Every effort has been made to correct the data presented to reflect actual wastes generated in San Bernardino County. These corrections are detailed in the footnotes to Table A (See page 3-13.) The amount of waste chipped may be listed on the manifest in gallons, pounds, tons (2000 pounds), cubic yards, liters, kilograms, metric tons (1000 kilograms), or cubic meters. In order to preparn an analysis of waste generation levels, all entries have been converted to tons. Ideally the data conversion should take into account the • physical properties of each individual waste. Aa a practical matter, that is not pos- sible. Thus a standard set of conversion factors were aced as reported in the Califor- nia Department of Health Services' Guidelines. In addition to the eonveraion of volume units to weight units, there is considerable uncertainty in the generatort' estimate of amount. More often than not, thece are estimates and do not reflect a precise measurement of amount, either volume or weight. As with any data management system of this magnitude, a small percentage of data entry error will oaur. In reviewing the San Bernardino County data, Department of Environmental Health Services staff found several types of data entry errors. Fizct, the magnetic tapes received, included a county code for each generator and for each treatment or disposal facility. It became obvious in reviewing a printout of the data that a number of generators were erroneously assigned the San Bernardino code. Those data records were deleted from the data analysis. It is not known how many San Bernardino county generators were erroneously assigned the wrong county code. Thus the reported data may underestimate waste generation levels. Second, one of the large hazardous waste generators in the county was not included in the data On checking with state personnel, it was learned that the generator had transposed two digits in his identifimtion number when preparing manifests. Be- cause manifest data regarding generators is entered by identification number, this erroneous number caused all of the manifest records for this company to be placed in a "suspense file". Had the erroneous number been a valid number, the waste records would have been attributed W another company with that particular number. Thus an error in the identification number would cause an error in the data even though • the manifest itself hsa the correct name and address on it. R'hile the data for this generator was corrected, it it difficult to identify the level of errors associated with identification numbers. 3-b As care be seen from the above diseuuion, then am numerous sources of uncertainty in the data, such that even the range of error is difficult to assess. Despite these un- certainties, however, the data provide valuable information which until now has not been available. The data clearly identify the types of waste generated in the county, the kinds of induetriec causing hazardout waste generation and how these wastes are currently being managed. 3.3 UNCERTAIIVTIES IId THE PROJECTIONS The previous action provided a discussion of the uncertainties in the data Un- certainties in the projections of futon waste generation levels also exist The largest uncertainty in projecting hazardous waste generation levels in the future occurs as a result of the rapidly changing regulatory climate and new technologies available to businesses. Due to inereaxd public concern and awareness of the problems of put management praetixe, the legislation which establishes the basic ground rules for treatment, storage and/or disposal of haurdouc waster has undergone considerable change during the last several years and is continuing to change dramatically. Due to these rapidly changing raquinments, steeply increasing fees and taxes, and un- certain future liability, many generators are changing their management practices in order to minimize their ux of hazardous materials and their generation of hazardous waste. Additionally, the technology available for waste reduction and on-site treat• roarer it also changing signi5eantiy. Given rhea considerable changes in both regulations and management practise, it is difficult to develop projeetone of future • waste generation levels. The "regulated univetx" is uncertain-both beeaux new regulations bring in new waste streams and also beaux there is no basis for pmjeet- ing generator': acceptance of new technologies or substitute materials. Prexnt trends suggest that hazardous waste generators are voluntarily incorporating waste minimization pnetioee into their operations, and/or are interacted in learning more about these opportunities. For that reason two projections are developed, one which incorporates an estimate of waste minimization efforts, and one which does not Tables FC - Q provide projections of hazardous waste generation levels to the year 2000. The assumptions used for each projection and the problems and uncertainties associated with each assumption an diseusxd individually with each Table. 3.4 DATA PRESEATATION This chapter, through a series of Figures and Tables presents quantitative data on hazardous waste generation and management in San Bernardino County during 1966 and 1967. While there are problems and shortcomings with the date as dis- cussed above, it should be emphasised that these Figures and Tables reflect consider- able time and effort on the part of DENS staff to verify and supplement the raw data provided by the California Departrnent of Health Services from its Haurdous Waste Information System. The Figures and Table presented here reflect, to the best of our ability, current knowledge of hazardous waste generation levels and management practices in San Bernardino County. All data sources are documented in the foot- notes to each Table, at an any calculations or assumptions uxd in arriving at the number pnxnted. • ,' 3.6 r~ U 3.4.1 Table A This Table shows the levels of hazardous waste shipped offsite for treatment andlor disposal by San Bernardino County generators in 1986 and 1987. The Table is organized by waste group, but includes individual waste categories within each waste group. The 17 waste groups were selected by the California Department of Health Services based on categories used in the report Hazardous Waste Manaee- ment: Recent Chanties and Policy Alternatives; Congressional Budget Office; 1985. All data in the Hazardous Waste Management Plan is organized using these waste groups. Waste groups used in this Plan do not preclude the use of new waste groupc (e.g. infectious waste) in the needs assessments of future amendments to the County Hazardous Waste Management Plan. Figure A illustrates graphiesliy the quantitati~•e data presented in Tabie A For il- lustrative purposes, Figure A shows Baghouse Wastes and Asbestos separately from the "Miscellaneous" Waste Group since these two waste categories contribute a sig- nificant percentage of the County's waste. On the other hand, Figure A includes other waste groups2 in the totals for "Miscellaneous Wastes' since these waste groups do not contribute a significant percentage of county wastes. • Significant differences between waste generation levels in 1986 and 1987 are ex- plained in the Notes on Table I. However, it should be noted that the signifcant dif- ference observed for the "Unspecified sludge" was caused by routine maintenance at a utility. The maintenance schedule for various utilities within the county may vary from 18 to 60 months. Figure A. Hazardous Waste Shipped OPfrite in 1986 and 1987 1,1eta1 containing bquids t.:,:, ,... e,x. ~,.:-.. ~.~..~.,.,. ..~ .. ,.;~:.<. ~M \tieak oil ..:::;;:::,,~;:.:,::>,,,.~~.:: gxys:a>: a~*ar,ioss»,.rcn Baghouse waste Tons Unspecified sludge Oih~sludgec Contaminated soil Tfiseellaneous wastes Non•halgentd.salvents 1~1eta1 containing sludges Asbestos 5000 10000 15000 ~a~~~~~ ~~ • 2Halogenated Solvenu, Organic Liquids, Pesticide. PCBs and Dioxins, Halogenated Organic Sludges and Solids, Non-Halogenated Organic Sludgy and Solids. Dye and Paint Sludge and Ruins. Non-metallic Inorganic Liquids and Non-metallic Inorganic Sludges 3-7 1966 ^ 1987 i ~ TABLE A • QUANTITIES OF s~e~aunOUS WASTE S81PPID OFFSITE IIV 1986 AND 1987 BY GENERATORS 1N SAN BERNARDINO COUNTY (1) Waste group (2) 1986 1987 See Primary treatment Tone Tons Note method (3) WASTE OIL 221 Waste oil & mixed oil 12,373.70 i 4 223 Unspecified oil eon- ~`` .+: twining waste 874.81 €~->fi12~3 subtotal 13,248.51 14,645.09 Oil recovery Her.OGENATID SOLVENTS 211 Halogenated solvents 137.49 ~" ;1~9 b0` 4 741 Liquids with halogenated _~`~~ organic cmpd. > 1000 mg/L 2 O8 s subtotal 139.57 191.62 Solvent recovery NON•HALOGENATID SOLVENTS 212 Oxygetutsd solventt 109.23 L~~; 213 Hydrocarbon solveatc 767.77 4 214 Unspecified solvent mixtures 1,888.40 subtotal 2,765.40 3,343.22 ORGANIC LIQUIDS 133 Aaueous with total organics > 1040 31.68 134 Aqueous with total organics < 1096 3..~ 341 Organic (noasolvents) with halogens 5.86 342 Organic liquids with metals 7,48 343 Unspecified organic ]iquid mixtures 261.95 subtotal 310.50 PESTICIDES 232 Pesticides and pesticide production waste subtotal PCBs & DIOXIIdS 261 Polychlorinated biphenylc 731 Liquids with PCBn50mg/L subtotal 0.42 0.42 ;L89 102.56 16.02 118.58 _.._.105.12 3-8 Solvent recovery Other rerycling Aq. trtment-organic Ineinention Table A • • • r 1 L J Waste group (2) OII.Y SLUDGES 222 OiUwater separation sludge 352 Other organic solids subtotal 1986 Tons 2,948.29 1,660.27 4,608.56 1967 See Primary treatment Tons Note method (3) 3,675;! ~......138~8p' 4,556.65 Oi] tteovery HALOGENATED ORGANIC SLUDGES & SOLIDS 251 Still bottoms with ~"" " halogenated organics .3:95; 351 Organic solids with ,~ ;~ '~ halogens 2.55 451 Degreasing sludge 187.31 ....,;,~.5~6' subtotal 189.86 27.21 Incineration NON-HALOGENATED ORGANIC SLUDGES AND SOLIDS >...: . 241 Tank bottom waste 1,290.92 x , ~$1~D 252 Other still bottom waste ~,Fr sus • 471 Paper sludge "`x#68: subtotal 1,290.92 463.54 2 Solvent recovery DYE & PAINT SLUDGES & RESINS 271 Organic monomer waste 272 Polymeric resin waste 281 Adhesives 291 Latex waste 461 Paint sludge subtotal METAL•CONTADYIIVG LIQUIDS 111 Acids with metals 221 Alkaline with metals 132 Aqueous with metala 723 Liquids with chromium >500 mg/L 3.00 _53.56 7.70 67.02 169.14 300.44 22,882.27 42.08 51.42 subtotal 22,975.77 °x+10' ~1'". 4:D7 ~ "LL"72. 248.03 METAL CONTAINING SLUDGES 171 Metal sludge 540.20 'I2S subtotal 540.20 2,126.45 3-8 Other recycling Other recycling Stabilization Table A Waste group (2) 1966 1967 Tons Tons NON-METALLIC INORGANIC LIQUIDS 112 Acid without metals 40.76 y ~~,37: s 113 Unspecified acid 10.70 , ~ ~yxS7..D2 122 Alkaline without metals 49.69 , {, ~45~& 123 Unspecified alkaline 90.46 ,;, ~ '" " "p'j 131 Aqueous with reactive ~;.; ".: anions 5.47 135 Unspecified aqueous solutions 57.60 "~Ql?~iT' 791 Liquids pH < 2 8.85 Y~`x"ft';D.79 ~ subtotal 263.53 384.28 NON-METALLIC INORGANIC SLUDGES 411 Alum & gypsum sludge 52.23 r~'`~~"%~bJ6:! subtotal 52.23 26.96 See Primary treatment Note method (3) L Aq. trtmt.-metals Stabilization COh"TAMINATED SOIL 611 Contaminated so0 2.556.57 "t45:~t2! subtotal 2,556.57 4,445.42 MISCELLANEOUS WASTES 141 Off-spec. inorganic 151 Asbestos 162 Other spent mtalyct 172 Metal dust 161 Other inorganic solid waste 322 Biologim] waste 331 Off-spec. organics 491 Unspecified sludge 511 Empty pesticide containers > 30 gal. 512 Other empty containers >30 gal 513 Empty containers < 30 ga] 541 Photoehemimis/phota processing waste 551 Laboratory waste 561 Detergent & smp 591 Bnghouse waste 612 Household waste subtotal 46.52 1,927.29 22.12 56.io 1,275.81 1.47 35.57 299.58 492.63 15.06 138.61 47.14 23.b9 5,751.89 19.12 10,1b4.70 Other recycling Stabffization Stsbffization Stab0ization other reryeliag Other reryeling Aq. trtmt-organic Other recycling 7 Stabilization Other rerycliag Other recycling Other recycling Other recycling Other recycling Other recycling Stabrlization Other reryeling i ~ TOTAL 59,S1b.76 69,718.79 B 3-10 Tnblc A • • • NOTES ON PREPARATION OF TABLE A (1) DATA SOURCES Data used in preparing this table was obtained from: a. California Department of Health Services Hazardous Waste Information Sys- tem (HWIS). b. San Bernardino County Department of Environmental Health Services files. c. When available, 1986 and 1987 Biennial Reports d. Telephone inter~~ews with individual generators, transporters, and faeiiities, as necessary. San Bernardino County DEHS obtained magnetic tapes of the California Department of Health Services HWIS date for hazardous wastes manifested into and out of San Bernardino County for the years 1986 and 1967. This data included the following in- formation: generator EPA identification number, generator county, generator name, generator address, generator city, facility EPA identification number, facility county, facility name, facility address, facility city, category of waste, treatment or disposal method, and amount of waste in tons. This data was printed out and reviewed. Data entries erroneousiy coded as San Bernardino county generators were deleted from the data base. CORRECTIONS FOR OUT•OF•STATE-SHIPMEh"TS - The data was corrected for out-of--state shipments as follows. The 1986 data obtained • from the state was supplemented by information provided by DHS in a memo dated August 26, 1987. The following additions were made. Waste Code 111 141 171 181 221 Tons added 7.43 2.06 12.64 0.51 30.02 Out-of-state shipments are already included in the 1987 data from the Hazardous Waste Information System, thus no additions were necessary. The data were also corrected for route service haulers as described in Note (4), below. (2) WASTE GROUP ASSIGNMENTS The various categories of waste were assigned to waste groups in axordance with Table A-3 of the Technical Reference Manual of the Guidelines for the Preparation of Hazardous Waste Manaeement Plans (TRM), June 30, 1981, California Department of Health Services, Toxic Substances Control Division, page A-7, (reprinted in Appen- dix D) with one exception. Wastes manifested as waste code 491, Unspecified Sludge, were moved from the recommended waste group "Non-Halogenated Organic Sludges and Solids" to "Miscellaneous Wastes". In San Bernardino County, these wastes are primarily inorganic residues from a treatment faolity or inorganic residues from a portable treatment unit and thus not appropriate in the recom- mended waste group. • (3) ASSIGNED TREATMENT METHODS Waste groups are assigned treatment methods in accordance with Table E-1, TRM, page E•9 (reprinted in Appendix D) with the following exceptions: the primary treat- 3-11 ment method for "Non-halogenated Organic Sludges and Solids" is shown as "solvent recovery" rather than "incineration'. Curnntly most of the wastes within that Waste Group are sent to neeyeling farilities. The primary treatment method for treating waste erode 491, unspecified sludge wastes, is listed ac "stabilization" rather than "in- cineration". These wastes are inorganic residues from earlier treatment processes. The primary treatment method for "Dye and Paint Sludges" is listed as "other reey- elin~' rather than "incineration". Appro~dmately 5096 of these wastes are eurnnt)y being recycled or used as an alternative fuel source. The primary treatment method for "metal-containing liquids" is listed as "other recycling", rather than "aqueous treatment-metals/neutralization". The bulk of wastes within that group are waste pickle liquor from the steel industry. These ferrous chloride solutions are con- centrated and sold to sewage treatment plants for use as a flocculent Additionally, pickle liquor, unspent acids and unspent alkalies have all been on the DH5 list of Recyclable Hazardous Waste Types (Section 66796, Title 22, California Code of Regulations) since 1985. Finally, the primary treatment method for "Contaminated Soil" is listed as "other recycling" rather than "incineration" in conformance with the other counties within the Southern California Hazardous Waste Management Authority. To the extent feasible, alternative treatment technologies developed in conjunction with the federal Superfund program will be encouraged. (4) ROUTE SERVICE HAULERS CORRECTIONS The data for this waste code wen corrected to take into account route healers using the modified manifest system. In California, the State Department of Health Ser- vices grants a variance from the full manifesting requirements for hazardous waste • haulers who transport such wastes as waste oils, dry cleaning solvents, and parts cleaners. This program is designed to promote recycling and to assist small businescea that generate any of the wastes listed above. The revised procedures al- low the transporter to prepare the manifest and combine wastes from multiple gener- ators. As a result, the transporter becomes the only "generator" of record in the HWIS data base. Because most route haul transportert operate in more than one county, the data base erroneously assigns all wastes handled by each company to the county where the transporter is based. In order to correct this data, DEHS staff con- tacted al] mute haul transporters known to operate in San Bernardino County, both those based in the county and those based in other counties. Although, every effort was made to develop a complete list of mute hauien operating within the county, omissions may have been made. The Table on the following page indicates the mute haulers contacted and the resulting changes made to the data. Most haulers were only able to give approximate percentages for each county's share of their business. (5) METAL-CONTAINING LIQUIDS Includes 22,660 tons~year of 111 Metal-containing liquid waste shipped from Califor- nia Steel Industries to Chemwest via pipeline. (6) NON-METALLIC IIVORGANIC LIQUIDS Includes 69.85 tons in 1987 from the HWIS suspense file. The waste was in the suspense file due to an error in reporting the generator EPA identification number. (See discussion on page 3-5.) (7) UNSPECIFIED SLUDGE • Unspecified sludge has been moved to Miscellaneous wastes and assigned a treat meet method of stabilization because these wastes are primarily inorganic residues from other treatment methods. - 3-12 • (8) DISCUSSION OF DISCREPANCIES For a discussion of large discrepancies between 1986 and 1987 data please see Notes for Table I. Corrections Applied to Table A to Account for Route Service Haulers Activities TRAIQSPORTER WASTE 1986 1987 MANIFESTING /GENERAT- CODE TONS TONS ING COUNTY Aztec Oil 221 1769.0 1769.0 San Diego/San Bernardino California Oil Recovery 221 1108.8 1106.8 RiversidelSan Bernardino Ca]ifornia Waste Oil Mgmt. 221 1419.6 1419.6 Los Angeles/San Bernardino Omega Oil 221 630.0 630.0 Los AngelesJSan Bernardino Prompt Oil Company 221 1554.0 1554.0 Los Angeles/San Bernardino Roadwest 221 252.0 252.0 Los Angeles/San Bernardino Rosemead Oi] 221 50.4 50.4 Los Angeles/San Bernardino Golden West 221 971.82 1222.54 San Bernardino/Los Angeles Golden West 221 1457.73 1833.60 San Bernardino/Riverside Golden West 221 2429.55 3056.34 S. Bernardino/San Bernardino West Coast Pumping 221 17.18 15.70 San Bernardino~LA & Orange West Coast Pumping 222 4.99 5.41 San Sernardino/I.A & Orange Base Oil 221 1230.62 1277.48 San Bernardino/Orange • Base Oil 221 964.66 1596.86 San Bernardino/Los Angeles Base Oil 221 24.62 31.94 San Bernardino/Riverside Base Oil 221 221.55 267.43 S. Bernardino/5an Bernardino Base Oil 221 1260 1260 San Bernardino/S. Barbara Base Oil 221 1260 ~ 1260 San BernardindVentura Safety Kleen 211 19.73 54.99 San Bernardino/Riverside Safety Kleen 213 524.75 643.37 San Bernardino/Riverside 'Safety Kleen 211 53.11 50.25 Duplicate due to transfer 'Safety Kleen 213 1186.06 1132.78 Duplicate due to transfer `The items marked with an `are wastes which were manifested from Highland to Reedley for retyeling after short-term storage in Highland. Since these wastes were manifested to Highland, and then again manifested when transported from Highland to Reedley, the data were corrected to remove double counting of these wastes. A similar correction is necessary for Base Oil shipments to and from the Base Oi] fa- cility. Since the discrepancy between the HWIS data and the figures reported by Base Oi] on its annual facility report are so great, the Base Oil totals were removed from the HWIS date and the figures from the annual report wen substituted. Those numbers are as follows: Base Oil: 1986: HWIS Total: 7714.52 T Annual Report: Collected:4981.65 T. Retycled:4491.89 T. • Base Oil: 1987: HWIS Total: 9796.33 T Annual Report: Co1)ected:5713.71 T. Retycled:5341.93 T. (The remainder was in storage at the facility.) 3-13 n Two other companies currently pick up hazardous waste in San Bernardino County using the modified manifest system. Oseo began this practice in 1988 and thus is not included in this Table. AAD began operating in San Bernardino County sometime during 1987 but was unable to provide information on amounts picked up that year. • • 3.14 5.4.2 Table B Table B provides a current rnunty needs assessment for commercial hazardous wade treatment andlor disposal capacity. This needs assessment assumes that all wastes within a given Waste Group in Table A will be treated by the primary tttatment method assigned for that particular waste group and will be treated within the county. Except for reryeling, each waste treatment method will produce some amount of residual which itself will require either further treatment, or proper dis- posal. The residual factors shown att taken from the Technical Reference Manual of the Guidelines for the Prevaration of Hazardous Waste Manaeement Plans. Figure B illustrates the data presented in Table B. Figure B. Required Treatment Capacity (Current Need) Other Recycling Oi] Recovery Stabilization • So]vent Recovery Aq. trtment- Metals/Neut. Incineration Ag. trtment-Organic 0 5000 10000 15000 20000 25000 30000 Tons • 3.15 1986 ~ 1987 C~ TABLE B • CURRENT COUNTY NEEDS ASSESSMENT FOA COMMERCIAL usvs~tnOUS WASTE TREATMENT/DLSPOSAL CAPACITY Treatment Method Required Treatment Capacity (1) 1986 Tondyear Aq. trtment-Organic 1.89 Aq. trtment-Metals/Neut. 263.53 Incineration 308.44 Solvent Recovery 4,195.89 Oil Recovery 17,857.07 Other Recycling 28,249.11 Stabilization 8,639.83 TOTAL b9,b1b.76 69,718.79 86/67 Average Tondyear 1.89 323.91 220.39 4,097.09 18,529.41 29,099.19 12,345.42 64,617.26 Residue] Factor (2) 1096 5096 1096 2096 2096 Table B Residuals Produced (3) 86/87 Avcragc Tondyear 0.19 161.95 22.44 819.42 3,705.88 • 12096 14.814.50 19,523.98 ~. (1) Based on data preaented in Table A, Quantities of Hazardous Waste Shipped Offsite, as assigned for primary treatment method. (2) Taken from "Technical Reference Manual of the Guidelines for the Preparation of Hazardous Waste Management Plans", June 30, 1986, California Department of Health Services Tonic Substances Control Division, Table E • 2, page E • 10. (3) Quantity of residue remaining atker treatment, requiring disposal. _J 3-16 .3.4.3 Table C r~ LJ • Table C presents information on existing commercial hazardous waste treatment facilities in San Bernardino County. The data presented is based on information pro- vided in a memo from the California Department of Health Services. Only two eom- mercial hazardous waste treatment farilities were operating in San Bernardino County during 1986 and 1987. Chemwest Industries operates a ferrous chloride reryeling facility which primarily receives waste pickle liquor (a solution of hydrochloric acid and iron) from a local steel mill. In the past, Chemwest has also received spent solution from the etching of circuit boards and electronic rnmponents. The wastes are neutralized and the fer- rous chloride is recovered for sale to municipal waste treatment plants. The DHS memo proaiding commercial facility capacities, identified Chemwest Industries' ac- ti4ities as "other recycling". To achieve consistency in treatment of the data, the wastes received by Chemwest Industries were also assigned to the "other reryeling" treatment method rather than "aqueous treatment-metalslneutralization" as shown in the Technical Reference Manual, Table E-1. This company has filed a notice of closure. The other commercial facility, Broco, Incorporated, specializes indisposing of off-spec, aged or surplus chemicals and explosives through detonation and burning. For lack of a better description, this company's treatment process is described as incineration. 3.17 TABLE C • COMMERCIAL HAZARDOUS WASTE TREATMENT FACILITIES IN SAN BERIVARDINO COUNTY Fscility Amount treated Treatment Capacity 1986 Tons (2) Method Tonslyear Bmco, Inc. 3.78 Indneration (3) 4.50 Chemwest Industries (4) 39,541.00 Other recycling 88,000.00 (1) Source: Sept. 30, 1967 Memo from California Department of Health Services, Toxic Substances Control Division (2) 1987 Data not available. (3) Broeo, Inc. specializes in disposing of primarily off•spee, aged or surplus chemicals and explosives through detonation and burning. (4) Includes both manifested wastes and wastes received via pipeline. This company has filed a notice of closure. ' Table C ~~ 3=16 • 3.4.4 Table D Table D compares the county's current hazardous waste treatment requirements (as shown in Tab]e B) with the county's existing hazardous waste treatment capacity, as shown in Table C. The diSerence between required treatment capacity and existing treatment capaaty is defined as current needs. The data presented in Table D is il- lustrated graphically in Figure D. Significant needs are shown for oil recovery, stabi- lization, and solvent reavery., Figure D. Comparison of Existing Commercial Treatment Capacity with Required Hazardous Waste Treatment Capacity Othcr Reryeling Oi] Ae~overy • Stabilization Solveat Aeoovay Aq. tnmeai-TfetaldNent Indneratioa Aq. trtmeat•Orgaaie 0 10000 20000 30000 40000 50000 60000 70000 80000 90000 Tons • 3-19 ~ Required capacity ~ Existing Capacity TABLE D -CURRENT COUNTY NEEDS ASSESSMENT FOR COMMERCIAL xe~e~OUS WASTE TREAT'MENT/DLSPOSAL CAPACITY Treatment Method Rq'd. Tneatment Existing Treatment Capadty Capadty (1) Capaaty (2) Exeeu (+) or Deficiency (-) 8687 Average 1986 Tons/year Tondyear Tondyear Aq. trtment-Organic 1.89 -1.89 Aq. trtment-Metals/Neut 323.91 -323.91 Incineration 220.39 4.50 -215.89 Solvent Recovery 4,097.09 -4,097.09 Oil Recovery 18,529.41 -16,529.41 Other Recycling 29,099.19 68000 58,900.61 Stabilization 12,345.42 -12,345.42 (1) From Table B -Current County Needs Assessment for Commerria] Aszardous Waste Treatment/Disposa] Capadty (2) From Table C - Commercial Hazardous Wade Treatment and Disposal Facilities in San Bernardino County (1987 data not available, but assumed to be the same as in 1986) Table D • • • 3-20 i 3.4.5 Table E Table E lists the quantities of hazardous waste imported into San Bernardino County during 1886 and 1987 as taken from the HWIS data. Figures reported for Base Oil and Safety Kleen have been corrected to include wastes picked up from other counties under the modified manifest system. Two companies, which are not identified in Table C, are shown as receiving manifested wastes. The first, D & M Drum Co., was a licensed facility in the past. The other company is TCl Burning Service. This company is a licensed facility for in- cinerating infectious wastes. Although infectious wastes are defined as hazardous wastes, they do not require a manifest for transport. These shipments att a subject of investigation. Figure E summarizes the data in Table E. It illustrates the amount of wastes im- ported into San Bernardino County and the counties where the wastes weft genera- ted. Most of the wastes imported into San Bernardino County came from Los Angeles, Orange, Santa Barbara, Ventura, and Riverside counties. • Figure E. Sources of Hazardous Waste Imported into San Bernardino County Los Angeles Orange Santa Barbara Ventura Riverside Unknown Santa Clara San Diego Fresno A)ameda Sacramento • 500 1000 1500 2000 2500 Tons 3000 3500 4000 4500 1986 ~ 1987 3.21 6 Table E • TABLE E - QUANTIT~S OF T;s~~RnOUS WASTE IMPORTED INTO SAN BERNARDINO COUNTY 1986 AND 1987 (1) Waste Waste County of Quantity of waste received Group Code Generation 1986 Tons BASE OII. SERVICES (2> Waste 221 Unknown oil Los Angeles Orange Riverside San Diego San Joaquin Santa Barbara Ventura 223 Santa Barbara Non-hlgtd 213 Unknown solvents Oily 222 Unknown sludges Los Angeles Orange Riverside _ Santa Barbara Misc. 331 San Diego BROCO, IIVC. Non-hlgtd 212 Riverside sa1vents Organic 343 Unknown . liquids Los Angeles Oily sludges 352 Loa Angeles Riverside Metal 171 Orange eludgea 0.45 0.06 0.01 0.05 369.20 1,474.44 1,512.10 35.65 0.83 1,260.00 1,271.54 0.62 4.57 16.86 14.34 Total 5,960.15 • 3.22 Table E • Waste Waste County of Group Code Generation Non-metallic Inorg.liquids 122 Los Angeles Misc. 141 Unknown Los Angeles Monterey San Diego 181 Unknown Los Angeles Ventura 331 Unknown Los Angeles Orange 551 Unknown Los Ange]es Orange Riverside San Diego San Francisco San Joaquin San Mateo Santa Clara 612 Alameda Quantity of waste received 1986 Tons 0.20 0.01 0.04 0.18 0.02 0.01 0.03 0.12 Total 1.18 i• CHEMWEST INDUSTRIES Metal cntng. 111 Unknown Liquids Alameda Los Angeles Orange Santa Barbara Santa Clara 121 Alameda Non-metallic Inorganics 112 Los Ange]es Orange 113 Los Angeles 272.22 224.62 860.89 33.35 57.54 217.96 13.92 20.85 201.41 Total 1,922.76 3.23 Waste Waste County of Group Code Generation D & M DRUM COMPANY Misc. 512 Unknown Kern Los Angeles Riverside Ventura SAb~Tl* BLEEN CORPORATION(2) Hlgtd. 211 Unknown so]vents Fresno Kern Los Angeles Merced Monterey Riverside Sacramento San Mateo Santa Clara Staniciaus Non-blgtd 213 Unknown Solvents .Fresno Loc Angeles Monterey Riverside Sacramento Santa Clara Sonoma 1 TCI BURNING SERVICE Non-hlgtd 214 Orange solvents oily sludges 352 Loc Angeles Miser 322 Los Angeles Total Quantity of waste received 1986 Tons .~9B7,~baa 19.73 4.62 524.87 Total 349.42 Table E • %;~ _• ~~ ~ _. 3-24 1,089.81 Table E r, Waste Waste County of Group Code Generation 551 Los Angeles Orange Total Total wastes imported Quantity of waste received 8,433.70 9,918.65 (1) Sources of information: s. California Department ofHea]th Services Hazardous Waste Information System b. Telephone interviews with route haulers • • (2) Corrected for route haul service, as discussed in Notes for Table A 3.25 3.4.6 Table F Table F lists the quantities of hazardous waste exported from San Bernardino County in 1986 and 1987, organized by waste group. The Table provides information on specific facilities receiving these wastes and the counties in which these facilities are located. Figure F summarizes this data by showing the amount of hazardous waste exported from San Bernardino County to other counties. Because of the limitations of the manifest data, a significant percentage of wastes are not assigned to any county for export The major increase shown in wastes exported to Imperial County between 1986 and 1987 reflects the opening of a new faolity in Imperial County during that time period. The shift in percentage of wastes shipped to Los Angeles County com- pared to Kings County reflects a shift in preference for treatment over land disposal, since there are no disposal facilities in Los Angeles County. Most of the wastes shipped to Kings County were for disposal. Figure F. Counties Receiving Haurdous Waste from San Bernardino County Generators Los Angeles Kings tinknown Imperial Santa Barbara San Diego Fresno Kern Riverside Out of State Contra Costa 0 5000 10000 15000 20000 25000 Tons' 1986 ~ 1987 • 3-26 Table F • TABLE F -QUANTITIES OF Re~sRTOUS WASTE EXPORTED FROM SAN BERNARDINO COUNTY, 1986 AND 1887 (1) ~i'aste Facility receiving County of Qty. recd. % of gen• Qty reed group waste Receipt 1986 tons eration(2) 1987 tons WASTE OIL American Envl. Mngmt. Sacramento 0.50 0.0096 Aztec Oil San Diego 1,769.00 13.35% California Oil Recovery Riverside 1,108.80 8.37% California Oil Recycle San Mateo 112.54 0.65% Cal. Waste Oil Mngmt. Los Angeles 1,419.60 10.72% Casmalia Disposal Santa Barbara 154.13 1.16% Chemical Waste Mngmt. Kings 602.60 4.55% Crosby 8 Overton Los Angeles 36.36 0.29% DeMenno/Kerdoon I.os Angeles 5,511.31 41.60% Dico Los Angeles 119.97 0.91% Evergreen Oi] Inc. Alameda I T Corporation Contra Costa 5.00 0.04So - Industrial Service Co. Los Angeles Leach Oi] Co. Los Angeles • Las Robles Cement Plant Kern 84.35 0.64% A4cCau]ey Oi] Co. Los Angeles 2,764.22 20.86% Nalco Oi] Refining Corp. San Diego OilgSolvent Process Co. Los Angeles 6.19 0.05% Oil Process Co. I.os Angeles 6.25 0.05% Omega Oil Las Angeles 630.00 4.76% Pacific Treatment Corp. San Diego Pepper Oil Co. San Diego 34.04 0.26% Petroleum Recycling Los Angeles 1.66 0.01% Petroleum Waste Inc. Kern 26.90 0.20% Prompt Oil Co. Ias Angeles 1,554.00 11.73% R 8 R Industrial Waste Las Angeles 14.94 0.11% Roadwest L.os Angeles . 252.00 1.90% Rosemead Oil Los Angeles 50.40 0.38% Rutherford Pacific Los Angeles 157.24 1.19% Talley Brothers Los Angeles 19.44 0.15% T~ip1e J Pacification Los Angeles 16.61 0.13% Unknown Unknown 1,240.83 9.37% W H Tank Lines Los Angeles 74.84 0.56% Western Asphalt Service Kern 17,775.92 134.17% OGENATED SOLVENTS Baron•Blakeslee Inc. San Diego 0.14 0.10% Bayday Chemical Santa Clara 7.69 5.51% Casmalia Disposal Santa Barbara 17.34 12.42% % of gen- eration(2) 12:08% 7:57% 0.17% 9.69cA 0.10% O:Q9% 0.37% 75.79% :3:03% 0:1'1% 0:26% 2:08% :::0.04% 1D8356 `:0`'1296 .:'0;76% 0:08% 4:3096 50:01% 'OAl% 10:815x, x1:22% 0.34% 0.1946 0:1196 fl.10% :..:':10.869n :::0..429e' 0.02% 151.92% 3 >1117% 3.27 22,248.65 Table F Waste Facility receiving County of Qty. recd. % of gen- group waste Receipt 1966 tons eration(2) Chemical Waste Mngmt Kings 5.17 3.70% Oi1&.Solvent Process Co. Los Angeles 24.23 17.36% Oi] Procesc Co. Los Angeles Omega Chemical Corp. Los Angelec Pacific Treatment Corp. San Diego Rho-Chem Loa Angeles 20.06 14.37% Roehl Corp. Loa Angeles 0.00% Romic Chemical Corp. San Mateo 14.89 10.67% Safety Kleen Corp. Fresno 53.11 36.05% Southern California Gas Los Angeles 0.04 0.03% Unknown Unknown 24.89 17.83% 167.56 120.05% 7~'OI~•HALOGEPIATED SOLVENTS Casmalia Disposal Santa Barbara 79.55 2.88% Chemical Waste Mngmt. Kings 17.51 0.63% Davis Chemical Los Angeles 1.00 0.04% DeMenno/Kerdoon Los Angeles 24.16 0.87% Dico Los Angeles 75.84 2.74% Eko Teck Ina Out of state General Portland Kern 126.74 4.56% Los Robles Cement Plant Kern 270.59 9.76% McAuley Oil Company Loc Angeles Nalco Oil Refining Corp. San Diego 4.17 0.15% Oi18Solvent Process Los Angeles 669.82 24.22% Oi] Process Co. . .Los Angeles Omega Chemical Corp. Los Angeles Pae~'ic Teatment Corp. San Diego R S R industrial Waste Los Angeles 3.3b 0.12% Rho-Chem Corp. Los Angeles 0.00% Romic Chemical Corp. San Mateo 14.58 0.53% Safety Kleen Fresno 1,186.08 42.89% Safety Kleen Orange Solvent Service Inc. Santa Clara Southern California Gas Los Angeles 0.39 0.01% Unknown Unknown 814.75 29.46% Western Asphalt Service Kern 0.00% 3,288.56 118.92% ORGANIC LIQUIDS Qty reed 1967 tons • • American Envl. Mn t gm Sacramento 1.20 0.39% ~m ~t0~S. . ~ w ~ 0:20%' Casmaiia Disposal Santa Barbara 7.25 2.33% . X3:0 25 ~.~~ .2,'J2~ Chemical Waste Mngmt Kings ~ `~ 69$5 ~ t `1865%' Crosby & Overton Loa Angeles `k"~~9 x."13%,: ~ DeMenno Kerdoon Los Angeles 204.48 65.86% qua x w; . ~ ~ ~$~~ • 9x ~` ~~.°l~% I T Corp. Los Angeles 0.31 0.10% '~~~` ~,~~~, z, '. i T Corp. ~ Contra Costa 11.92 3.84% ~~ii ;a X1.1B~i! % of gen- eration(2) i:oe96 i>19.3396 ' 9.14% A.314e '~ A.0896 ..'.:7.4944 '':.3.06% s ::2632% 0.03, ,<.:17.249n 95.15% 3 3-26 109.44% 3 •«' t F l as e aci ity receiving County of group waste Receipt McAuley Oil Company Los Angeles Nelco Oil Refining San Diego Oil&Solvent Process Co. Los Angeles Oil Process Co. Los Angeles Omega Chemical Corp. Los Angeles Pacific Treatment Corp. San Diego R & R Industrial Waste Los Angeles Romie Chemical Corp. San Mateo Unknown Unknown PESTICIDES Casmalie Disposal PCB's & DIOXIIZS American Envl. Mngmt Chemical Waste Mngmt General Electric Co. North American Envl. Retro Service Inc. • U S Ecology Unknown. OII.Y SLUDGES American Envl. Mngmt Atchision, Topeka & SF BKK Sanitary Landfill Casmalie Disposal Chemical Waste Mngmt Crosby & Overton DeMenno/Kerdoon Dico Envirosafe Services I T Corp. McAuley Oil Oil &Solvent Process Co. Oil Process Company Pacific Treatment Corp. R & R Industrial Waste Rutherford Pacific Southern California Gas U S Ecology • Unknown W H Tank Lines Table F Qty. recd. 40 of gen• Qty recd 96 of gen- 1986 tons eration(2) 1987 tons eration(2) .`2.24 0.59% '1145 ...0.12% 26.68 8.59% 36.66 "9:7996 `a.S2 0:169'0 _..b.45 0:12% 9.58 3.0940 D 43 0.11% _. '0.08 0.02% 1:02 02796 49.08 15.81% 27.40 7,2gy6 310.50 100.00% 374.04 99.3340 Santa Barbara 0.42 100.0096 __ 3589 100:DD% 0.42 100.0040 1.89 100.0040 Sacramento Kings Orange_ Los Angeles Sacramento Out of state Unknown Los Angeles Los Angeles Santa Barbara Kings Los Angeles Los Angeles Los Angeles Out of state Contra Costa Los Angeles Los Angeles Los Angeles San Diego Los Angeles Los Angeles Los Angeles Out of state Unknown Los Angeles 22.22 18.7491, 16:03 :11:93 50.16 42.3240 i~:69 22.91 19.3240 +19;1$ 8.53 7.1940 0.00% X1.30 14.36 12.119'0 32:9;1 118.20 99.6846 105.12 0.25 0.014'0 325.22 7.0640 1,516.96 32.92% 260.65 5.66% 11.25 0.24% 18.06 0.39% 4.37 0.0940 5.04 0.1196 5.89 0.13% 0.11. 0.00% 2,463.87 0.41 4,612.06 3-29 53.46% 0.01% 100.08% '15:25% "D:88% ;;iS6096 ~6:774e 0.299fo 31'.1140 100.00% '0.0096 24.7140 ,sio% la:~s = D,05Se 8:65% 100.10% Table F Waste Facility receiving County of Qty. reed. % of gen- Qty reed % of gen- group waste Receipt 1986 tans eration(2) 1987 tons eration(2) HALOGENATED ORGANIC SLUDGES Casmalia Disposal Santa Barbara 188.86 99.4796 ':.B.~G2 ° `30.9496 Chemical Waste Mngmt Kings `37;86 :66:0140 DeMennolKerdoon Los Angelec :.0:83 3:05% Oil & Solvent Process Co. Los Angeles 1.00 0.53% 189.86 100.0096 27.21 100.0040 NON-HALOGENATID ORGANIC SLUDGES American Envl. Mngmt Sacramento D.094o Casmalia Disposal Santa Barbara 23.81 1.8496 4.42% Chemical Waste Mngmt Kings 1,064.22 82.4440 Ss+ii4a Crosby&Overton Los Angeles 28.56 2.2140 '..,24:52% DeMenno/Kerdoon~ Los Angeles 42.65 3.3096 ` 365496 Dico Los Angeles 1.98'b I T Corporation Contra Costa 67.06 5.2096 '36:5040 McAuley Oil Los Angeles 8.00 0.629'0 2.50% Ne1eo Oi] Refining San Diego 1.40 0.1196 Oil 8 So)vent Process Los Angeles 33 1396 Pacific Treatment Corp. '3x540 Triple J Pacification iL"219fo Unknown Unknown 55.20 4.28% 5:4fi% 1,290.92 100.00% 463.54 100.0040 DI'B 8 PAIIQT SLUDGES 8 RESINS Casmalia Disposal Santa Barbara 127.37 42.39% 713x6 +45.7096 Chemical Waste Mngmt Kings 97.72 32.5340 N'48:85 19:70% Oil b Solvent Process Los Angeles 79.50 26.4640 `23x2 13:3940 Pacific Treatment Corp. San Diego ;36x4 ! .:14:619n R 8 R Industrial Waste Los Ange]es 3.15 1.0540 0 ~ ! 0.78% Southern California Gas Los Angeles 0.27 0.09% ~ ~ Triple J Pacification Los Angeles Y .: x OS ,0.834c Unknown Unknown 3.85 1.289'0 '°y ; 73 X41 .3.41% 311.86 103.80% 247.56 99.82% )lIETAL CONTAINIIVG LIQUIDS ' Casmalia Disposal Santa Barbara 83.86 0.36% Chemical Waste Mngmt Kings 121.58 0.53% Crosby 8 Overton Los Angeles I T Corporation Contra Costa Oil Process Co. Los Angeles Pacific Treatment Corp. San Diego 2.08 0.0196 Philipp Bros. Chemicals Los Angeles 56.70 0.25% Southern California Gas Loa Angeles , Tripe J Pacification Los Ange]ec Unknown Unknown 31.55 0.1496 295.77 1.29% r1 LJ • • 3-30 Table F • • ~t'aste Facility receiving County of group waste Receipt NON-METALLIC IIVORGANIC LIQUIDS American Envl. Mngmt. Sacramento Casmalis Disposal Santa Barbara Chemical Waste Mngmt Kings DeMenno Kerdoon Los Angeles I T Corporation Contra Costa Olin Hunt 5perislty Los Angeles Oil & Solvent Process Los Angeles Omega Chemical Corp. Los Angeles Pacific Treatment Corp. San Diego Philipp Bros. Chemicals Los Angeles Triple J Pacification Los Angeles Unknovrn Unknown METAL CONTAINING SLUDGES Aonics Corp. Los Angeles Casmalia Disposal Santa Barbara Chemical ~'Vaste Mngmt Kings Gould Inc. Metals Div. Los Angeles National Solder Los Angeles Philipp Bros. Chemicals Los Angeles Quemetco Inc. Los Angeles Unknown Unknown Qty. recd. 1986 tons 0.62 108.67 0.78 23.75 62.63 12.99 8.50 14.61 0.24% 41.24% 0.30% 9.01% 23.77% 4.93% 3.23% 5.62% 20.36 7.73% 253.11 96.05% % of gen- Qty reed % of gen- eration(2) 1987 tons eration(2) NOI~'-METALLIC INORGANIC SLUDGES Chemical Waste Mngmt Kings 0:1040 .:;25.82% L28% 1:13% fl.3496 1S:?3% 3.1640 13:87'la 26.29 COI~TAMIIvATED SOIL American Envl. Mngmt Sacramento Atchision Topeka 8 SF Los Angeles Casma]ie Disposal Santa Barbara Chemical Waste Mngmt Kings I T Corporation Imperial Oil & Solvent Procesc Los Angeles Petroleum Waste Inc. Kern Southern California Gas Loa Angelec Unknown Unknown U S Ecology Out of date 83.73% _. _ .._ '0.66 .:' '33:113% 84.72 15.68% ;.`;x89.26 , 4~0% 353.02 65.35% '063:19 2:974r .~tls. .,. IL95~b ;..1."19 31015, 3.66 0.68% ` ; '? 53 >, '0.35% ., . 98.80 16.29% ,..>,~;'695R6 ' 7502% 540.20 100.00% 2,126.45 100.00% 52.23 100.00% 16.J6 i00OD% 52.23 100.00% 26.96 100.004c 0.40 0.02% :123-02 `' 2.77~k 527.95 20.65% :812.20 18.27% 1,587.42 62.Q9% ~37b:S2 `: 30.9440 198.59 7.77% ;277 I8 6.249c 0.83 0.03% '~ ~ x xF x 29b 1~ =456 336 :3 M~b ~p 217.56 8.51% ~s'~~3 22' ~ 60.8996' 23.62 0.93% '~'~_'`"~1214. .,p-'fi(!<b z,sss.s7 loo.oo% a,44s.42 loo.oo% 3-31 Table F Waste Farility receiving group waste MISCELLANEOUS American Envl. Mnmgt. Anderson Solid Waste Appropriate Technology BKK Sanitary Landfill Bayday Chemical Casmalie Disposal Chemical Waste Mngmt Crosby & Overton Eko Teek Inc. Envirosafe Services Forward Ina Gould Inc Metals 1 T Corporation I T Corporation J D Brodine 8 Son National Environments] Northwest Enviroservice Oil 8 Solvent Process Omega Chemical Corp. Pacific 'IYeatment Corp. Philipp Bros. Chemicals R & R Industrial Waste Southern California Gas Triple J PaciSeation T S M Recovery & Ree. Unknown U S Ecology County of Receipt Sacramento Shasta San Diego Los Angeles Santa Clara Santa Barbara Kings Los Angeles Out of state Out of state San Joaquin Loc Angeles Imperial Los Ange]es Los Angeles San Joaquin Out of state Los Angeles Los Angeles San Diego LOS Angeles Loc Angeles Los Angeles Los Angelet Los Angeles Unknown Out of state Total wastes Qty. reed. 1986 tons 0.81 1.50 1,261.30 0.32 858.75 6,834.27 0.05 0.00% 0.25 0.00% 3.52 0.03% 1.47 0.22 761.15 12.64 9,736.25 40,667.79 % of gen- Qty recd % of gen- eration(2) 1987 tons eration(2) 0.01% 0.01% 12.42% 0.00% 8.46% 67.30% 0.01% 0.00% 7.50% 0.12% 95.88% 68.36% 52,301.26 ?5.02% • (1)Data Source: California Department of Health Services hazardous Waste Information System. (2) R of generation .amount shipped to facility/total amount of waste group shipped offsite by San Bernardino County generators. (3) Corrected for route hnuler service. • • _~ 3-32 • 3.4.7 Table G Table G identifies commercial hazardous waste storage capacity in San Bernardino County. Commercial storage capacity includes all hazardous waste facilities ]ixnsed to accept for storage purposes wastes from other generators, i.e. wastes generated offsite. These wastes are then shipped for treatment or dispose] elsewhere. The San Bernardino County Household Hazardous Waste Collection Centers are listed with the commeraa] hazardous waste storage facilities. Although these Cen- ters provide storage capacity, they sccept only household hazardous wastes. r~ L_J • 3.33 Table G TABLE G - COMNIERRCIAL He7e~0US WASTE STORAGE CAPACITY • AND ACTIVITY (1) Facility Storage Ave. qty. Storage 96 Storage Method in storage eapadty eapsdty >9o day. used Tons Tons Base Oil Service SO2 Tank 21 330 6.496 Safety Kleen Corp. SO2 Tank 1,147 2,088 54.996 SOl Containers 22,900 11,000 100.0% San Bernardino County Household Hazardous SOl Containers Varies 42 Variec (2) Waste Collection Center • (1) Sources: e. 1966 data taken from memo from California Department of Health Services b. 1986 data taken from March 23,1968, letter from Robert P. Warhsmuth, Safety Klecn Corp. (Safety Kleen's storage eapaaty is dependent on process capacity at Reedley Recycle Center and how often material is picked up at Highland.) (2i Capacity based on storage of 30 drums at each of six sites. 3-34 • 3.4.8 Table H Ci' Table H presents information about the on-site treatment andlor disposal of hazard- ous waste in San Bernardino County, both in summary form for all on-site fadlities and broken down by facility. Figure H-1 illustrates the information presented in Table H. Figure H-2 compares the data from Table A (hazardous wastes shipped offsite) with the data in Table H (hazardous wastes managed on-site). Approximate- ly S~ro of the hazardous wastes generated in San Bernardino County are shipped offsite for treatment andlor disposal. This figure is believed to be comparable to na- tional figures for the relationship between wastes managed on-site and offsite. Figure HI. On-Site TYeatment/Disposal, by Method Aq. trtmt. 1,ietalsRQeut. A q. t r e a tm e n i• O rga n i c Residuals Disposal Other Recycling Stabilization • Incineration Solvent Recovery I Io Ioo iooo ioooo Iooooo Iooooo0 Tons (Logarithmic scale) Figure H•2. Comparison of On•site Treatment/Dispocal with OPfsite Treatment!Dicposal in San Bernardino County 52240 • ~ Otf--site Treatment/Disposa] ~ On-site Treatment/Disposal 61,617.28 Toni 1,179,755.7 Tow 3.35 94.7896 TABLE H•1 - ON-SITE TREATMENT/DLSPOSAL OF HAZARDOUS WASTE IN SAN BERN.4RDIN0 COUNTY -1986 TOTAL, ALL FAr'**-rrrrra (1) Generalized Quantity Capadty of 96 of treatment treated/disposed treatment capacity method on site method used Tons Tons Aqueous treatment-Organic 554,690.0 2,132,600.0 26.0196 Aqueous treatment- Metal s/Neutralization Incineration Solvent Recovery Oil Recovery Other Recycling Stabilization Residuals Disposal TOTAL 614,562.6 3,203,703.0 19.1896 8.7 104.0 8.3796 4.9 87.3 5.6196 293.0 300.0 97.6796 220.5 1,050.0 21.0096 3,976.0 132,130.0 5.0196 1,173,755.7 b,469,974.3 21.4696 (1) Sawces of Information: a. California Department of Health Services Memos b. 1986 Facility Annual Reportt c. Responses to San Bernardino County DENS Survey d. Telephone interviews e. San Bernardino County Department of Health Servieet filet Table H • • 3-36 Table H • TAB LE FI-2 - ON-SITE TREATMENT/DISPOSAL OF Re~sstnOUS WASTE IN SAN BERNAFtDINO COUNTY - 1966, BY FACII.TI'Y Facility / Generalized Quantity Caparity of % of Source of SIC Code Treatment trtd/dispsd treatment capacity information/ Method on-site method used see note Tons Tons A/3499 Aqueous treatment•M/N 440.0 2,085.0 21.1% 1 s., 2 B/4013 . Land Application (Disposal) 3,833.0 132,130.0 2.9% 1 s., C/4013 Aqueous treatment-Org 1,680.0 2,100.0 80.0% 1 d.,2 0/3312 Aqueous treatment-Org 538,010.0 2,100,000.0 25.6% 1 e. Aqueous treatment•M/N 606,692.0 3,171,400.0 19.1% E~2819 Aqueous treatment-M/N 1.7 504.0 0.3% 1 e.,2 F/3799 Aqueous treatment M/N I3.3 50.0 26.6% 1 a&b Incineration 8.7 104.0 8.4% 1 a&b Stabilization 220.5 1,050.0 21.0% 1 a&b • G/3429 Aqueous treatment-Org 15,000.0 30,500.0 49.2% 1 e: H/1061 Other recycling 293.0 300.0 97.7% 1 s. Aqueous treatment-M/N 2,200.0 12,000.0 18.3% 1 a&e I19711 Aqueous treatment-M/N 4.6 85.2 5.4% 1 d. J,'1422 Disposal (Landfill) 143.0 unknown 1 e. R/3692 Solvent recovery 2.1 21.0 10.0% 1 e&b Aqueous treatment-M/N 5,208.0 17,556.0 29.7% la&b Aqueous treatment-M/N 2.1 21.0 10.0% 1 b. IJ9711 Solvent recovery 2.8 85.2 3.3% 1 a. M/8734 Aqueous treatment-M/N 0.9 1.8 50.1% 1 e. TOTAL 1,173,755.7 5,469,993.2 (1) Sources of information a. California Department of Health Services Memo, November 20, 1987 b. 1986 Facility Annual Reports, as available c. Response to San Bernardino County Departrnent of Health Services survey, 1987 d. Telephone interview • e. San Bernardino County Department of Health Services files (2) TreatmenUdisposal method no longer in use, alternative technology now applied 3.3? • 3.4.9 Table I Table I presents information about the sours of hazardous waste generation. Each of the waste categories is divided into one of the following sources: a) Clean up wastes, excluding underground storage tank removals; b) Wastes generated by removal of underground storage tanks; c) Route service hauler wastes; d) Wastes generated by large hazardous waste generators (>12,000 kg/year); e) Wastes generated by email quantity generators (<12,000 kg/year); f) Miscellaneous. wastes which include houcehold hazardous wastes, non- hazardous wastes and those wastes for which the origin mould not be determined. Table I also includes two estimates: one for small quantity generator waste not cap- tured by the regulatory program and one for household hazardous waste not collected by the Household Hazardous Waste collection program. The final column of Table I calculates a planning estimate of hazardous wastes routinely generated in San Bernardino county. This planning estimate is obtained by subtracting clean-up wastes (including tank removals), from the 1986 and 1987 to- tals, averaging the two years' data, and adding the small quantity and household hazardous waste estimate. Organization of Table I • Ideally, Table I would be printed on a large poster-size sheet, configured as shown in the diagram on the next page. Instead, Table I is printed on nine separate pages. An index is provided here to assist in reviewing the Table. Pages 3-40, 3-41, and 3-42 present data for Total wastes manifested in San Bernar- dino County (from Table A), clean up wastes and wastes generated by removal of un- derground storage tanks. Pages 3133, 3.44, and 3-45 provide data on wastes carried by route haulers, as well as the routinely generated wastes produced by small and large generawrs. Pages 3-46, 3-47, and 3.48 provide data on miscellaneous wastes, estimates of addi- tional small quantity generator wastes and household hazardous wastes and the planning estimate derived from all previous columns Figure I illustrates the relative proportion of each of these categories for the average of the 1986 and 1987 totals, except for tank removal wastes which are for 1987 only. The additional small quantity generator estimate and household hazardous waste estimate are also shown. The figure illustrates the relative importance of each of the sources of hazardous waste generation. • 3-38 r1 U • T.ble 1 • Stuhlyear 1'lannin[ Filinrle of Quaetlliea; er Naardouc ~t'ale Shiyped Oatlle a b c d a e f [ • A 1 ~ k 1 1 I I I 1 t I I I I 1 I I I I I I I I I I I I 1 I I I I I I I I I I 1 I 1 I I I 1 I I I I I I I I 1 I I I I I I I I I I I I I I P.dc3•s0 I I I I 1 I I I I I I I I I I I P.[c3•l3 I I 1 I I I I 1 I I I I I I I I I I I A[e3•K 1 I I ' I I I I I ~ I I I I I I I I ~ I I ~ I I ~ ~ I I I I I ; ~ I I .I I I I _, I I I I 1 1 I I , I I I , I I I , I I I i I I I I I I I , I I I , 1 I I , I I I , I I I 1 I I 1 I I I ~ I I I I 1 I I I I I I I 1 I I 1 I I ~ I 1 I I I I 1 ~ 1 I I I I I I I 1 , I I Pa[e3•[3 I i I I Pa[c3•N I I I Pge3•<7 I I ~ 1 I , I I I , I I I I I I I , I I 1 , I I , '~ 1 1 I I I 1 , I I 1 , I I 1 , I I I I I I I , 1 1 1 , I I I I I I I I I I I I I I I I I. I I 1 I I I I I I I I I I I I I I I 1 I I 1 1 ; I I ELI ~.. I 1 ; I ~_~ 1-•~- I I I I I -I.L~T Patc 3 • ~3 Pa[c 3 • t5 M[e 3 • ~[ a. Waste group b. Total quantity manifested c. Clean up wastes (except UST) d. Tank removal wastes e. Route service hauler f. Large generators (>12,000 kg/yr) g. Small generator (<I2,000 kg/yr) h. Miscellaneous wastes i. HHW estimate j. SQG estimate k. Planning estimate 1. Totals Figure I -Sources of Offsite Shipments of Hazardous Waste (including esti[nates) U Large generators SQG (estimate) Route hauler Clean-up wastes Tank removal HHW (estimate) SQG (setusU Miscellaneous 3.39 0 5000 10000 15000 20000 25000 50000 35000 40000 45000 Tons Table I • TABLE I • MULTI-YF.AIt PLANNING ESTIMATE OF QUAIQTTr1ES OF Ae~eRTOUS R'ASTE SHIPPED OFFSTfE Total qty. mnifsted. (1) 1986 1987 Tons Tons ~t'ASTE OIL 221 VGaste oi18 mixed oil 12,373 70 14;32:66:. 223 unspecified oil rnn- taining waste 874 Bl 612.3 subtotal 13,248.51 14,645.09 Clean-up wastes (2) 1986 1967 Tons Tons 14.21 320: 528.14 "i101~7 542.35 222.75 Tank rmval. castes. (3) 1986 1987 Tons Tons 110.25 `-436.05 1.66 155:34 111.91 591.39 AAI.OGENATED SOLVENT'S 211 Halogenated solvents 137 49 :11&9:50 .41 Liquids with halogenated a organic cmpd.>1000mg/L 2 OB '~ .` ..<2~2 subtotal 139.5? 191.62 ti0?~•HALOGENATED SOLVENTS ' '0.10 0.10 ":0:33 0.33 212 Oxygenated solvents 109 23 ~.~9 0.84 % w ~ ~'' 4.44 2.91 213 Hydrocarbon solvents 767 77 ~ ~30~9: ~x~d~`x~s69 1.47 6L7 214 linspec. solvent mixtures 1.888 40 °J7~.'7~Y! 2.96 ,x1.99: 14.42 _.~B.S. ~ subtotal 2,765.40 3,343.12 3.80 33.68 122.71 20.33 ORG4NIC LIQUIDS . 133 Aqueous with total ~, y;>, '¢;;< ~,„_,~~, N:; organics > 104c 3168 ~ ;' x`~,LS, ,,1 Z5, 8.34 134 Aqueous with total '"" N "` ~ organics < lOSc 3 53 ~ :f ~~ 3.53 ~>;~ ?7.11 341 Organic (nonso]vents) ! w ~ ~~~th halogens 5 86 .~-~ r:~~ a +~ `~ 342 Organic liquids with r metals ? 48 ~_,~ iP ' m {m 343 L'nspeeified organic z„ ~ ~''~~~~'~' liquid mixtures 26195 .~.:. 0.'71'< 111.30 ~'~`:°4~'-17; '3b•U3 subtotal 310.50 376.55 114.83 55.52 8.34 133.14 PESTICIDES 232 Pesticides and pesticide ~~,.~; ~= ~~ ~', z production waste 042 _ 0.42 ; ~_ subtotal 0.42 1.89 0.42 1.69 PCBs and DIOXLNS 2fi1 Polychlorinated biphenyls 102 66 ~ ` 102.56 ',~°~ ~~1.1~ .,,,~,,~.. ~~,~' 731 Liquids with PCBs>50mg/L 16 02 ~.~~ 0~8i 16.02 'ate , 0.913; ~ ,~..::s„~~ : :J subtotal 116.58 105.12 118.56 105.12 . 3-40 Table I • Total qty. mnifsted. (1) Clean-up wastes (2) Tank rmvnl. castes. (3) 1986 1987 1966 1987 1986 1987 Tons Tons Tons Tons Tons Tons OILY SLUDGES 222 OiUwater separation sludge 2,946 29 ,3,$71.35'. 246.10 3.53: 7.54 226 21 352 Other organic solids 1,660.27 $85.30 516.51 13.02 . 0.63 216.08 subtotal 4,608.56 4,556.65 762.61 16.55 8.17 442.29 H.9I.OGENATED ORGANIC SLUDGES & SOLIDS 251 Still bottoms with halogenated organics L95 351 Organic solids with halogens 2,55 951 Degreasing sludge 187.31 25~SI .......::. subtotal 169.86 27.21 NON-uaT_OGEIhATED ORGANIC SLUDGES AND SOLIDS 291 Tank bottom waste 1,290 92 '461.~t1; 1,041.77 ` 3.75 60.9 :350:06 252 Other still bottom waste _ ~~ 326 971 Paper sludge ;' .0;$g , subtotal 1,290.92 463.54 1,041.77 5.01 60.9 350.06 8 PAINT SLUDGES & RESINS 2.1 Organic monomer waste 300 ~.~0'', 272 Polymeric resin waste 53 58 41:841 5.05 261 Adhesives 7 7p .~~I 291 Latea waste 67.02 ,»31:72 461 Paint sludge 169.14 I82.00' ~` 0.45 0.61 0:6 subtotal 300.44 248.03 5.05 0.45 O.Bl 0.6 ~IETAL•CONTAINING LIQUIDS 111 Acids loth metals 22,88227 .22,766$+l` 0.12 121 Alkaline with metals 42 OB ~ x.`71( 132 Aqueous Kith metals 5142 xj.25~,2; 38 35 X0 04 .23 Liquids with chromium . . >500 mg/L .219.'32! 37.56 subtotal 22,975.77 23,113.59 38.47 67.60 1\lETAL COIr"TAINiNG SLUDGES 171 Meta] sludge 540 20 ,.,~"126,~~: 1;331.18: subtotal 540.20 2,126.45 1,331.18 NOti-METALLIC IIJORGANIC LIQUIDS 112 Acid without metals 40 76 57! x"` 3 0 12 13 Unspecified acid ~ 10 70 . . '°~67~12; . ~, 22 Alkaline without metals 49 69 ~ r°4$ $S ! ' ~;~ 123 Unspecified alkaline 90.46 . . '53.30 ~. ',1.~', 3.41 ~~ Table I • 131 Aqueous with reactive Total qty. mnifsted. (1) 1986 1987 Tons Tons Clean-up wastes (2) 1986 1987 Tons Tons anions 5.47 " "~3! 135 Unspecified aqueous solutions 57.60 '207.40" 9.i8 791 Liquids with pH < 2 8.85 r. 3'«,079 €" subtotal 263.53 384.28 0.12 10.63 1~'OIC•METALLIC INORGANIC SLUDGES Tank rmval. wstec. (3) 411 Alum & gypsum Budge 52.23 '~" "26 96 subtotal 52.23 26.96 SOIL ... ...:. 611 Contaminated soil 2,556.57 ,4;445.4;2 2,392.12 , 3134.33 164.45 '131Y:79 subtotal 2,556.57 4,445.42 2,392.12 3,134.13 169.45 1311.29 ~IISCELLANEOUS WASTES 141 Off-spec. inorganic 151 Asbestoc 162 Other spent catalyst 172 Aletal dust 181 Other inorganic solid waste 322 Biological waste 331 Off-spec organics 491 Unspecified sludge 511 Empty pesticide containers > 3U gal. 512 Other empty containers > 30 gal. 513 Empty containers < 30 gal. 541 Photoehemical/phoW- 46.52 1,927.29 22.12 58.10 1,275.81 1.47 35.57 299.56 492.83 15.06 processing waste 138.61 551 Laboratory waste 4T.14 561 Detergent 1!r soap 23.59 591 Baghouse waste 5,751.89 612 Household wastes 19.12 subtotal 10,154.70 33.33 1,927.29 10.61 17.06 1.26 2.15 19.45 2,011.15 TOTAL 59,515.76 69,718.79 7,03L2? 1.29 1.29 • f. 6,537.18 381.39 3044.08 • 3-42 Table I • TABLE I ~ (continued) Route service hauler (4) 1986 1967 Tons Tons ii'ASTE OII. 221 Vraste oil 8 mixed oil 9,434.90 .1D,12757 223 unspecified oil con- taining waste subtotal 9,434.90 10,127.57 HALOGENATED SOLVENTS 211 Halogenated solvents 24.93 88:29 .41 Liquids with halogenated organic cmpd.>1000mg/L subtotal 24.93 68.29 Gen.>12,000 kglyr (5) Gen.c12,000 kg/yr (6) 1986 1987 1986 1987 Tons Tons 11 Tons Tons 2,224.54 3,`068.'8~:e,b 282.52 _95.53 321.62 "334;69 23.39 17.83 2,546.16 3,403.54 305.91 113.36 94.46 8824 18.10 32.54 2.08 Z.'32 96.54 90.36 18.10 32.54 NON-HALOGENATED SOLVENTS 212 Oxygenated solvents • 213 Hydrocarbon solvents ~ 662 90 84i 40 90.26 97.86 54.97 377.91: a,b 13.69 5.54 :9:61 18:83 214 tinspec. solvent mixtures 1,801.79 1;`787JQ9 69.23 x,92:49 subtotal 662.90 841.40 1,989.91 2,220.37 88.46 120.93 ORGAiVIC LIQUIDS 133 Aqueous with tots] organics > lOSs - 23.34 134 Aqueous with total organics < 104'0 '~`1 ~8; ;3;12 341 Organic (nonsolvents) . with halogens $K~ 1.26 !~.$3 4.56 342 Organic liquids with metals ~ ~~ 7.48 0.45 343linspecified organic ~ _ -' liquid mixtures ~' 136.80 33B.+I?' 13.85 `..31:94 subtotal 161.42 152.38 25.91 35.51 PESTICIDES 232 Pesticides and pesticide ;; rrti~ production waste subtotal PCBs and DIOXINS 261 Polychlorinated biphenyls 731 Liquids with PCBs>50mg/L subtotal a"" ~. ra 3-43 Table 1 Route service hauler (4) 1986 1987 Tons Tons OII.Y SLUDGES Gen.>12,000 kg/yr (5) 1986 1987 Tons Tons Gen.<12,000 kg/yr (6, • 1986 1967 11 Tons Tons 222 Oil water separation ~ "' .,: sludge 1094 ~'~~F~,92,79 2,66814 .3,300.70',e 15.5T.4832 352 Other organic solidc ';~E X~v 1,128 13 62&86':e 15.00 :1217 subtotal 10.94 92.79 3,796.27 3,929.56 30.57 60.29 HALOGENATED ORGANIC SLUDGES & SOLIDS 251 Still bottoms with ~'~~ .~': halogenated organics "" ~~ ~ "! .2'35. 351 Organic solids with , ' "~ aai, . Y halogens v~ ~ 2 55 ` 451 Degreasing Budge 167 31 " ~ '36~6,e subtotal 189.86 27.21 1 ON•HALOGENATED ORGANIC SLUDGES AND SOLIDS 241 Tank bottom waste ~° '~"'~~"~ . 180 63 '86~ 7.62 252 Other still bottom waste " e?y,y r ~ av~ ' `u 471 Paper sludge ~ r } fr'~" ° '~~~ subtotal 180.63 87.23 7.62 DYE 8 PAI2QT SLUDGES 8 RESINS 271 Organic monomer waste 272 Polymeric resin waste 261 Adhesives 291 Latez waste 461 Paint sludge subtotal `~ r. 300 44 71 , °~9a89; 3 82 ~x ¢'`:'~' 7 70 66.94 >><„'~0Z7 0 OB 149.61 :`..3.41:1 18.52 261.46 201.66 33.12 214 21. i _. q .2141, ~`n~ ~5 a v. ~S ..`:1:45 `.37:00 42.80 I~fETAL COl~'TAII~TING SLUDGES 171 Metal sludge zM x ~ ^e~ 516.97 ,~86:'S3+e 10 59 . , H.4~1 subtotal 516.97 786.83 10.59 8.44 NON•1<1ETALLIC INORGANIC LIQUIDS 112 Acid without metals 40.24 ~.,a 113 Unspecified acid 10.42 ' 0.28 ~ ~5~ 122 Alkaline without metals 46.45 324 ~:. 123 Unspecified alkaline ~ wn ~' 70.89 „„.,m~8` 19.57 ~<<°~33,1- 3 - 44 M • • Table 7 Route service hauler (4) Gen.>12,000 kg/yr (5) Gen.Q2,000 kg/yr (6) 1986 1987 1986 1987 1966 1987 Tons Tons Tons Tons 11 Tons Tons 131 Aqueous with reactive anions 5.4? s> $34 135 Unspecified aqueous solutions 28.25 195.64:b 24.16 2.56 791 Liquids with pH < 2 8.65 .D.79' subtotal 210.57 356.24 47.65 17.41 1 O?~-METALLIC INORGANIC SLUDGES 411 Alum & gypsum sludge 52.23 26:98 subtotal 52.23 26.96 SOII. 611 Contaminated soil subtotal hLISCELLANEOUS WASTES 141 Off-spec. inorganic 151 Asbestos • 162 Other spent catalyst 172 Meta] dust 161 Other inorganic solid waste 322 Biologics] waste 331 Off-speeorganics 491 Unspecified sludge 511 Empty pesticide containers > 30 gal. 512 Other empty containers > 30 gal. 513 Empty containers < 30 gal. 541 Photochemica]/photo- processing waste 551 Laboratory waste 561 Detergent S soap 591 Baghouse waste 612 Household wastes subtotal 10.92 22.12 5B.10 1,239.96 17.27 271.65 489.06 15.04 138.61 16.40 5,751.89 8,031.02 0.21 16.69 1.47 1.24 25.36 1.62 0.02 11.29 57.92 i ~ i ~ TOTAL 10,133.67 11,130.05 40,960.51 48,136.03 628.25 554.66 • 3-45 Table I • TABLE I • (continued) Misc. wastec (7) 1966 1987 Tons Tons R'ASTE OII, 221 Waste oil & mixed oil 307.21 ~:~>T6388' 223 Unspecified oi) con- " " u R'3n taining waste 'x:60' subtotal 307.27 186.46 HALOGENATED SOLVENTS 211 Halogenated solvents 741 Liquids with halogenated organic cmpd.>1000mg/L subtotal Estimated Estimated Planning HHW (8) SQG (9) Estimate (10 ) Tons Tons Tons 800.00 8,190.00 21,652.54 350.06 800.00 8,190.00 22,202.60 163.28 2.10 165.38 NON-HALOGENATED SOLVENTS 212 O d l ~ : '` 1 8 46 192 63 • xygenate co vents > > 0 . . 213 Hydrocarbon solvents > ; 153.22 1,155.75 214 Unspec.solvent mixtures ` ..:~~ 492.08 2,369.19 subtotal . 4.03 753.76 3,717.76 ORGANICLIQUIDS - 133 Aqueous with total '~''°~,; A °` organics > 1046 ,q~ 84.61 96.26 134 Aqueous with total ~~~ ~ organics < 1040 x: ~ ~ . 7.60 341 Organic (nonsolvents) y '' with halogenc . x_„ 3.85 342 Organic liquids with ~~`: metals 3.97 343 Unspecified organic >~>< = liquid mixtures ~> . „ ;?• ;.;.'..<`'M' 580.00 740.53 subtotal b80.00 84.61 652.22 PESTICIDES 232 Pesticides and pesticide production waste 100.00 145.76 245.76 subtotal 100.00 145.76 245.76 PCB s and DIORII~IS • _ 261 Polyeh]orinated biphenyls 731 Liquids with PCBv50mg/L ~.;>,.~~;;::..~~'<:t subtotal ~ " 3 - 46 • Misc. wastes (7) 1986 1987 Tons Tons Table I Estimated Estimated HHW (8) SQG (9) Tons Tons OII.Y SLUDGES 222 OiVwater separation i; _.... sludge 3,068.13 352 Other organic solids 15.17 2.39 902.05 subtotal 15.17 2.39 3,970.19 HALOGENATED ORGANIC SLUDGES & SOLIDS _.. _ 251 Still bottoms with halogenated organics 351 Organic solids with halogens 451 Degreasing sludge subtotal NON-HALOGENATED ORGANIC SLUDGES AND SOLIDS 241 Tank bottom waste 252 Other sti]] bottom waste • 471 Paper s]udge _ subtotal D1'E 8 PAIiQT SLUDGES & RESINS 271 Organic monomer waste 272 Polymeric resin waste 281 Adhesives 291 Latex waste 961 Paint sludge subtotal 1\SETAL-CONTAIIJLNG LIQUIDS 111 Acids with metals 7.43 121 Alkaline with metals 132 Aqueous with metals 723 Liquids with chromium >500 mg/L subtotal 7.43 hIETAL CONTAINING SLUDGES 171 Metal sludge 12.64 subtotal 12.64 .NON-METALLIC INORGANIC LIQUIDS 112 Aeid without metals 113 Unspecified acid 122 Alkaline without metals 123 Unspecified alkaline 2.50 r '10:'7fi' 10.76 3.47 50.00 0.98 138.11 138.11 1.28 106.29 138.11 246.65 Planning Estimate (10 ) Tons 146.02 0.34 148.36 2.70 45.19 3.89 44.37 32.20 206.84 32.20 302.98 2,696.70 25,571.10 21.90 44.46 90.88 50.00 2,696.70 25,728.35 0.39 668.12 0.39 668.12 21.11 50.00 187.61 276.47 47.76 71.16 C~ Misc. wastes (?) 1986 1967 Tons Tons 131 Aqueous with reactive anions 135 Unspecified aqueouc solutions 791 Liquids with pH < 2 subtotal C~ Estimated Estimated HHW (B) SQG (9) Tons Tons 18.25 50.00 205.86 Table I • Planning Estimate (10 ) Tons 25.16 125.32 4.62 571.80 NON-METALLIC INORGAPIIG SLUDGES 411 Alum 8- gypsum sludge ''" 3.15 42.75 • subtotal 3.15 42.75 SOIL 611 Contaminated soil - subtotal IrIISCELLAh'EOUS WASTES 141 Off-cpee. inorganic 2.06 151 Asbestaa 162 Other spent catalyst 172 Metal duct 161 Other inorganic solid wade 8.51 322 Biological waste 331 Otf-spec organics 491 Unspecified sludge 511 Empty pesticide containers > 30 gal. 512 Other empty containers > 30 gal. 513 Empty containers < 30 gal. 541 PhotochemicaUphoto- processing waste 551 Laboratory waste 561 Detergent S soap 23.59 591 Baghouse waste . 612 Household wastes 19.12 subtotal 53.28 TOTAL 380.62 ~ 1~ 1- 05s00 24.94 11.06 • 58.68 212.79 1,190.22 0.74 26.39 3,167.48 25.00 70.15 70.41 388.42 134.b8 130.60 25.00 413.54 305.70 21.84 35.95 6,073.69 16.84 11,528.69 12~ 7 70-9 • _ ;i 3-46 • NOTES ON TABLE I (1) Data Sources The 1986 and 1987 Totals were taken from Table A (Transfer station wastes were removed in Table A as described in Notes on Table A.) In an effort to systematically analyze the raw data obtained from the California Department of Health Services Hazardous Waste Information System, DENS staff verified and supplemented the data supplied. Three new fields wen added to each record: a field identifying the reason for waste generation, and two fields (if necessary) to identify the four digit Standard Industrial Classification (SIC) Code for each county generator. The follow- ing choices were used as a basis for waste generation: C =Clean up wastes other than underground storage tank removal (All PCB wastes and asbestos wastes were designated as dean-ups) T =Underground storage tank removal R =Routinely generated wastes, > 12,000 kglyear S =Routinely generated wastes, < 12,000 kglyear F =Permitted commercial hazardous waste facility H =Wastes "generated" by route haulers using the modified manifest system N = A'on-hazardous waste shipped to a Class I disposal facility =Unknown, can not be determined This new information was used in the preparation of Table I as described below. • (2) Clean up wastes These columns include wastes from clean ups including asbestos removal, PCB removal, emergency response and other clean up efforts. Clean ups of leaking underground storage tanks are not included. Asbestos removal and PCB removal are included as clean up wastes because there are no businesses ih San Bernardino county routinely .generating these wastes. Rather, these materials are being removed as the result of regulator}• requirements and must be disposed of as hazardous wastes. (3)Estimated wastes from removal of leaking underground storage tanks. Data from the California Department of Health Services Hazardous Waste Information system was supplemented with information in the San Bernardino County Department of Emzronmental Health Services underground storage tank removal logs to provide an estimate of clean up wastes specifically generated from the removal of underground storage tanks. This estimate is low because during 1986 and 1987 tanks which had been triple rinsed could be transported without a manifest Additionally, it is possible that some rinsate and tank bottom waste was shipped via a route hauler on a modified manifest. While most of the waste included here was shipped under aone-time identifi- cation number, the estimate does include wastes shipped under established identifi~a- tion numbers, as well. Thus, these figures reflect only individually manifested wastes from tank removals, not total wastes from tank removals. It should be noted that about 205r of the tank removals in 1986 and about 4096 of the tank removals in 1987 could be matched with individually manifested wastes. The sharply higher waste levels in 1987 may be attributed to either more tank removals in that year and/or increased use of the manifest system compared to 1986. • Most contaminated soil from removal of leaking underground storage tanks was left on- site for treatment and, thus, is not included in these figures. Despite a change in the 3-49 CJ rules of the South Coast Air Quality Management District, on-site treatment continues to be the treatment method of choice for this particular waste category. (4) Wactec transported by routs cervice haulea These figures are corrected for out-of-county hauler and shipments. Because of the manifesting procedure, these wastes can not be assigned to any specific group of genera- tors (neither < non 12,000 kg/yr). (5) Large generators These columns show total wastes produced by generators producing > 12,000 kglyear, exe)uding clean up wastes and removals of underground storage tanks. (6) small quantity generators These columns show total wastes produced by generators produring < 12,000 kg~year and manifested offsite, excluding clean-up wastes and removals of underground storage tanks. For projections of additional wastes generated by small quantity generators, see pages 3 - 46, 3 - 47 and 3.46 of the Table. - (7) Miscellaneous wastes These columns include the following categories of wastes: a) Undetermined origin, company is now out of business b) Non-hazardous waste sent to a Class I facility including: Waste Code 1966 Tons 1987 Tons 161 8.00 16.00 ' 561 23.59 48.00 c) Household hazardous waste manifested from the county Household Hazard ous Waste Collection Centers. Noa-hazardous waste sent to Class I facilities In order to determine whether any additional non-hazardous wastes generated in San Bernardino County are managed by hazardous waste facilities, county businesses wen screened as to whether they might generate any of the "special wastes" identified in Se~- tion 66740, Titie 22 of the Code of California Regulations. The following special wastes were found to be generated in San Bernardino County: 1) Ash from burning of fossil fuels, biomass, and other combustible materials 2) Auto shredder waste 3) Baghouse and scrubber wastes from air pollution control 4) Cement kiln dust 5) Tailings from the extraction, benificiation and processing of ores and minerals. Of these wastes, the auto shredder waste is being treated on-site under a variance and is being disposed of in a Class III landfill. At the present time, the bnghouse waste is classified as hazardous and is included with the wastes listed in Tables A - J. Based oa • information in DENS files, none of the other categories of special wades are being sail to a hazardous waste facility. 3-50 n U One other category of waste is generated in San Bernardino County which may affect these figures. The wastes generated in cleaning internal utility boiler surfaces to re- store heat transfer capability is currently being managed as hazardous waste. The utili• ty has expressed interest in having this waste "declassified" so that it may be managed as non-hazardous waste. Since an acceptable characterization has not yet been eom• pleted, these wastes are also included with the wastes listed in Tables A - J. (8) Estimated household hazardous waste The estimate of total household hazardous waste generated is based on an estimate of 7.5 pounds/year/household of household hazardous waste generated by 430,947 households in the county. The 7.5 pounds/year/household estimate is taken from a study done by researchers at the University of Arizona for the Association of Bay Area Governments entitled A Characterization of Hazardous Household Wastes in Marin County. The number of households was obtained from 1968 estimates made by the Pop- ulation Research Unit, California Department of Finance. The total figure was then fur- therbroken down to waste groups by determining approximate percentages of waste oil, corrosive, flammable, toxic, and oxidizer wastes collected at the Household Hazardous Waste Collection Centers as reported in Department of Environmental Health Services Household Hazardous Waste Proeram Year in Review, Fiscal Year 1987-1986, Septem• ber 198fi. Waste categories were assigned to waste groups as t~'aste Cateeorv • Corrosives Oxidizers Flammables Paints Toxics Batteries Miscellaneous (Phosphorous, sulfur, etcJ Waste Group Non-metallic inorganic liquids Non-metallic inorganic liquids Organic liquids Organic liquids Pesticides Aods with metals Non-metallic inorganic solids (9) Small quantity generators, estimated waste In addition to the waste individually manifested offsite (shown on pages 3 - 43, 3 - 44, and 3 • 45 of the Table) an estimate of additional wastes from small quantity generators (SQG) was made using the "no survey" method as outlined in the DHS Guidelines for the Preparation of Hazardous Waste Manaeement Plans. Ideally, one of the survey methodologies should be used to provide a more accurate estimate of SQG generation levels and management practices. However, because of time and budget constraints, this was not possible. The "no survey" methodology is based on two independent estimates: 1) the number of small quantity generators within the county for each type of business which may generate hazardous waste, and; 2) the amount of hazardous waste generated by each business. • The California Department of Health Services has identified businesses likely to genera- te hazardous waste by SIC code, a Standard Industrial Classification system developed by the federal government. The Department of Health Services has also provided an estimate of the total waste generated per generator for each type of business as well as a 3-51 percentage breakdown by type of waste.. A bibliography of sources used to derive these i figures is provided in the Technical Reference Manual. The number of small quantity generators was estimated by comparing the number of each type of business permitted by San Bernardino County Department of Environmen• tai Health Services with the number of businesses reported for San Bernardino County in Southern California Business Directory and Buyers Guidel, and in Microeosm2. Waste amounts were then calculated using the figures given in the Technical Reference Manual for each type of business. There are several sources of error introduced by using this method of estimation. The waste amounts assigned for each business by the Department of Health Services reflect some average amount and do not take into consideration the size of the business. Businesses within the county range from e' single ownerwperator to a business with 100+ employees and yet both are assigned the same total waste generation factor. Ob• viously businesses on opposite ends of this spectrum will generate different amounts of waste. It is not known whether or not the range of business sizes and their distribution within San Bernardino County is similar to that of the national survey on which these figures are based.. Another source of error is the fact that several of the penentage breakdowns for the waste estimates add up to greater than 10040. For example, wholesale and retail sales outlets are lisud sa produdng the following wastes with percentages as shown: Ignitable paint wastes 1296 • Ignitable wastes <19b Spent solvents 1896 Strong acids or alkalies 1196 Waste pesticides 796 Other 9540 14496 Although each retail sales outlet (again, regardless of size) is assigned 0.7 metric tons~year, because of the sheer number of such facilities, this discrepanry causes eonsid• erab]e uncertainty. The estimate of the number of businesses within each category may not be accurate in part because of the large number of new businesses forming and others going out of business. Additionally, the Dun i Marketing Services provides an individual listing for each business by name. Many businesses appear to operate under several names, caus- ing duplication of listings and thus double counting of those businesses. This method of estimation auumes each business generates hazardous waste, however, that may not be the case. For example, several categories of businesses are listed within the vehicle maintenance grouping. This assumes that each of these perform their own vehicle maintenance services. In fact, many may use commercial vehicle maintenance services and thus may not generate hazardous waste at all. According to one national 1 Southern California Business Directory and Buyers Guide, Los Angeles Area . Chamber of Commerce, TMP Publishing, Newport Beech, CA, 1988. 2 Microcosm, Dun's Marketing Services, 1986. 3-52 study of small quantity generators done for the U. S. Environmental Protection Agency,3 the percentage of businesses within these inridental SICs which actually gen- erate hazardous waste is between 20 and 4096 of the total number of businesses within the category. Finally, it should be noted that about 9296 or 11,600 tons of the wastes included in the SQG estimate are either waste oil, solvents or lead and batteries. These wastes may be legally transported either on a modified manifest or in the ease of lead acid batteries, with no manifest at all when chipped to a reeyeler. Consequently, the inclusion of these wastes may be a duplication of wastes already shown in the column for route hauler ser- vice and/or may include wastes which are being properly managed even though the gen- erator is not currently under permit with the Department of Environmental Health Ser- ~~ces. According to the Abt Associates study, 6096 of the waste generated by small quantity generators is lead acid batteries, 909'0 of which are recycled. (10) Planning estimate This column represents the present baseline of waste currently generated in San Bernardino County requiring off-site treatment and/or disposal. It was obtained by sub- tracting clean-up wastes and tank removal wastes from the total wastes generated for each respective year and averaging the 1986 and 1967 remainders. The estimated wastes from small quantity generators and households were then added to the 1986 - 196 7 average to obtain this column. • (11) Discussion of maior difYerencec between 1966 and 1987 data After clean up wastes (including those resulting from underground storage tank removals) are subtracted from the yearly totals, several waste categories remain which show large differences between the two years' data. Each of these waste categories was reviewed to determine the specific generators who were the source of these differences. The reason for each difference was then determined either by file review or telephone in- terviews with individual generators. While many generators were responsible for the differences six different reasons for the wide variation between the 1986 and 1987 fig- ures emerged as typical. These are summarized below. a) Increased awareness • better compliance The DENS generator enforcement program has been operating since 1963, with an em- phasis on both educational assistance and regulatory compliance. The increased awatt- ness of regulaWry requirements and the use of proper waste management practices by county generators have resulted from routine inspections by field inspectors. This has led to an apparent increase in hazardous waste generation levels in the county over the past six years. Frequently businesses will have large quantities of regulated waste stored on their property either because they are unaware that it should be managed properly or they simply don't know what to do with this waste. It is not uncommon to have a large amount of waste manifested following a first inspection. This waste has resulted from an accumulation of many years and thus to some extent skews the data. On the other hand, there att moct likely additional companies which DEHS inspectors have not reached yet which att also storing waste. Thus, these accumulated wastes should be considered in the planning estimate, and in fact, have been included as routinely generated wastes. • 3 National Small Auantity Hazardous Waste Generator Survev, Abt Associates, Inc., Cambridge, MA. 1985. 3.53 b) Growth San Bernardino rnunty has undergone rapid growth and development over the past several years. Areas once rural and sparsely populated are rapidly becoming urbanised. Along with population growth, the county has also experienced major economic develop- ment. As s result new rnmpanies which have located in the county are responsible in some ways for the higher levels of waste generation as well as for more diversity in the type of wastes generated. Existing companies have also benefited from economic devel- opment and some have had increased waste generation because of increased production. c) Change in Maaegemeat Practices There are several instances when a major change in management practices-usual)y to institute waste minimization procedures-has led to significant changes both in the amount of waste generated and in the types of waste generated. For example, in one in- stance, a comparry has removed an evaporation pond and installed a filter press. As a result the company is now regularly shipping sludge wastes, whereas earlier it did not Another example is a company which has switched from toivent-based adhesives to water-based adhesives. Earlier that company shipped solvents and other organic K•astes, whereas now they are not ' d) Intermittent Waste Generation There are several instances, primarily involving utilities, where hazardous wastes are generated as the result of the maintenance of equipment These maintenance schedules may range from 18 to 60 month cycles. As a result, although the waste is routinely gen• crated, figures from any given year are not typical and some correction factor needs to • be developed for planning purposes. e) Change in regulatory requirements The number and type of wastes which are defined at "hazardous" have changed over the years. These changes an also reflected in the data. In one instance, a company is shown as generating a large quantity of waste in 1987 but not 1986. In fact there was no change in the generation of the waste, but rather in the reporting and tracking re- quirements. In 1986 the waste was not required to be manifested, while in 1987 it was. f) Military There are several instances where major changes in waste levels and types were the result of military aetivitiec. Further information is not available. 3-54 n U 3.4.10 Table J Table J presents information on the general business source (by Standard Industrial Classification, SIC, code) of all routinely generated wastes. S1C codes were assigned to each business based on information in San Bernardino County DEHS files. Figure J-1 illustrates the data from Table J regarding wastes managed offsite. The major industrial sources of hazardous waste generation in the county are: the pri- mary metal industries, utilities, railroad transportation, and fabricated metal pro- ducts. Wastes in the "unknown" and "miscellaneous" categories make up a sig- nifieant fraction of the wastes generated. (Since wastes recycled following route hauler pick-up come from a variety of industrial sectors, these wastes were listed with unknown wastes rather than in the route hauler's industrial classification.) Figure J•2 provides a similar summary of the wastes managed on-site. The major in- dustrial sources of hazardous waste are the primary metal industry, fabricated metal products and railroad transportation. Manufacture of electronic equipment and met- al mining also contribute significant)y. Figure Jl. Industrial Sources of Hazardous Wastes Managed Offsite • ~~ ~J Primary metal industries i,::, Unknown i.,._ ,~:a Utilities Railroad transportation ~ 1966 Misc. Military~a ~ 1967 Fabricated metal prod. 1~on•metallic mineralst~,l Chemicalsdsllied prod. ~~,, ~ ~ ~ 0 5000 10000 15000 20000 25000 30000 Tons Figure J2. Industrial Sources of Hazardous Wastes Managed Oa• site Primary Metal Industry Fabricated Metal Prod. Railroad T~ansportetion Electronic Equipment Mete] Mining Misc. 100 1000 10000 100000 1000000 10000000 Tons (Logarithmic scale) 3-55 Table J u TABLE J -INDUSTRIAL SOURCES OF fisvestnOUS WASTES SIC CODE: 10 -Metal 1VIining Waste Group Waste Managed Oncite Waste Oil Aletal-Containing Liquids 2,200.0 Afetal-Containing Sludges 293.0 Aliscellaneous Wastes 181 SIC 10-Total 2,493.0 Waste Managed Offsite SIC CODE: 14 -Non-Metallic Minerals, ezceptfuelc Waste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids Oily Sludges Dye 8 Paint Sludgea & Basins Non-metallic Inorganic Liquids D4iseellaneous Wastes 141 181 331 512 513 551 591 SIC 14 -Total 233.43 0.20 570.58 23.34 350.74 0.50 1.03 1.22 143.0 21.11 5.22 1I7.67 0.68 1.03 143.0 1.326.95 SIC CODE: 16 -Heavy Construction, ezcluding Building Waste Oi] 1.66 Non-Halogenated Solvents Oily Sludges 1.68 Tiiscellaneous Wastes 512 SIC 16 -Total 3.54 -'s z~~. <' . ~¢ ~~~>«. X85. 35.63 3-56 i C~ Table J • ~i'aste Group Waste Managed Onsite SIC CODE: 17 -Special Trade Contractors Waste Oi] Halogenated Solvents Icon-Halogenated Solvents Organic Liquids Oily Sludges Dye 8- Paint Sludges & Resins Jvon-metallic Inorganic Liquids A4iscellaneous Wastes 161 331 512 551 SIC 17 -Total SIC CODE: 20 • Food and Biadred Products Kon-Halogenated Solvents Dye g Paint Sludges & Resins !~4iscellaneous Wastes b51 SIC 20 -Total SIC CODE: 24 -Lumber and Wood Products Waste Oil IQon•Halogenated Solvents Oily Sludges Dye & Paint Sludges & Resins D1eta1-Containing Sludges SIC 24 • Total SIC CODE: 25 -Furniture and Fizturec Halogenated Solvents Non•Halogenated Solvents Oily Sludges Dye S Paint Sludges & Resins Metal-Containing Liquids • SIC 25 • Total Waste Managed Offsite 1986 (1) 1987 (1) Tons Tons 0.3? 40.74 0.84 2.91 0.44 0.08 45.38 20.01 20.01 10.42 2.29 10.50 2.62 7.57 33.40 3):37 `'a s ~ <~> .....:`c:A~:'tnn 2.27 ~.Iip <~ 3112 `.~.SS ' '' ~~{.'4 ':^ry yiT= 12.35 2.16 7.11 1.14 0.84 11.25 23.19 3-57 Table J R'aste Group Waste Managed Waste Managed Offsite Onsite 1986 (1) 1987 (1) Tons Tons SIC CODE: 26 -Paper and allied products Waste Oil 102.57 Non-Halogenated Solvents 266.83 ':.: ,162,;39 Organic Liquids . ... 4 ... X7°93 Oily Sludges ~3~7 Dye 8 Paint Sludges & Resins 47.53 w: Miscellaneous Wastes k.,- ~ "h 331 2.96 £'H ~`~ ' SIC 26 -Total 418.81 237.00 SIC CODE: 27 -Printing and Publishing • ~~'aste Oi] ;.:..:,3117:. non-Halogenated Solvents 100.47 - ~Dii.id Oily Sludges ~° ~fi Non-Halogenated Organic Sludges "6.67:' r Dye & Paint Sludges & Resins z'°"0~$ 3.36 ~~ Aiscellaneous Wastes x ~~~ ~, ''"~ • 181 ~1` 331 , f ~"~1.942 491 , ~ `~ ~~1: SIC 27 -Total 103.83 139.58 SIC CODE: 28 -Chemicak and allied Prodnctc R'sste Oil Halogenated Solvents 5.24 :von-Ha]ogenated Solvents 502.68 Organic Liquids Oily Sludges Non-Halogenated Organic Sludges 0.84 Dye & Paint Sludges & Resins 61.59 Aietal-Containing Liquids 1.7 Non-metallic Inorganic Liquids 0.20 ASiseellaneous Wastes 181 847.48 491 51.90 512 115.55 b13 8.50 5s1 o.so SIC 28 • Total 1.7 1,814.68 ~. 3-58 Table J • Waste Group Waste Managed Waste Managed Offaite Onaite 1986 (1) 1987 (1) Tons Tons SIC CODE: 28 -Petroleum and Coal Products Waste Oi] 68.23 ~~128 Non•Halogensted Organic Sludges ~6~B' hiiscellaneous Wastes w~?~; 181 SIC 29 • Total 68.23 80.10 SIC CODE: 30 -Rubber and Miscellaneous Plastics products Waste Oi] 22.24 ;~7,~ Halogenated Solvents 3.26 Iron-Halogenated Solvents 9.65 ~, Oily Sludges 5.04 , x:49 Dye g Paint Sludges & Resins g.~ ~ ?, ~ Non-metallic Inorganic Liquids . { Misce]laneousWastes ~~s ~`zs-. - 491 "n^0~5 • SIC 30 -Total 49.52 60.07 SIC CODE: 32 • Stone, Clay and Glaze Products Waste Oi] 72.94 Halogenated Solvents Non-Halogenated Solvents Organic Liquids 4,58 Oily Sludges 1.05 Dye 8 Paint Sludges 8 Resins Non-metallic Inorganic Liquids 3.12 Miscellaneous Wastes 491 10.42 512 0.22 551 SIC 32 • Total 82.33 SIC CODE: 33 • Primary Metal Industries Waste Oil 51.64 Halogenated Solvents Non•Halogenated Solvents b.83 rganic Liquids 538,010.0 ily Sludges O.Q9 Meta]•Containing Liquids 606,692.0 22,680.00 3-59 Table J «`aste Group Metal-Containing Sludges Non-metallic Inorganic Liquids Miscellaneous Wastes 181 ' b61 591 SIC 33 • Total • Waste Managed Waste Managed Ollsite Onsite 1966 (1) 1967 (1) Tons Tons 112.05 ...>:.$Bi46 30.84 .11746 T: ::<.~~ ~:°i: "" '3395 23.59 ~' a 48:'00. b,751.89 6:370:53 1,144,702. 28,656.13 29,502.51 SIC CODE: $4 -Fabricated Metal Products Waste Oi] 340.13 Halogenated Solvents 11.42 ?von-Halogenated So]vents 316.01 Organic Liquids 15,000.0 Oily Sludges 92.78 Non•Halogenated Organic Sludges 27.93 Dye & Paint Sludges & Resins g,gg ASetal-Containing Liquids 440.0 126.42 Tietal-Containing Sludges 5,54 Non-metallic Inorganic Ligttidc 36,33 Aiiscellaneout Wastes 141 172 181 192.96 491 220.23 512 0.50 551 SIC S4 • Total 1b,440.0 1,381.14 SIC CODE: 36 • Industrial Machinery and Equipment R'aste Oil 3.57 Non-Halogenated Solvents 3q,9g Oily Sludges Dye 8 Paint Sludges & Resinc 31.59 Aietal-Containing Liquids Non-metallic Inorganic Liquids 25.26 Miscellaneout Wastec 141 512 2.64 513 0.15 SIC 35 • Total 98,20 ,: ~: ~: ..: F. Upc'T<t~:~ i30' ,~. ;~ a y 134.74 .~ 3-60 1,390.62 • Waste Group Waste Managed Waste Managed Offsite Onsite 1986 (1) 1987 (1) Tons Tons SIC CODE: 36 -Electronic and other Electric Equipment Waste Oil Halogenated Solvents Non-Halogenated Solvents Oily Sludges Halogenated Organic Sludgec Dye g Paint Sludges & Resins Metal-Containing Liquids Metal-Containing Sludges Non-metallic Inorganic Liquids I~'on-metallic Inorganic Sludges Miscellaneous Wastes 172 181 491 512 551 SIC 36 • Total 2.1 5,210.1 5,212.2 • SIC CODE: 37 • Transportation Equipment ~i'aste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids 6.7 Oily Sludges Non•Halogenated Organic Sludges Dye & Paint Sludges 8 Resins Metal-Containing Liquids 233.8 Meta]-Containing Sludges Non-metallic Inorganic Liquids Miscellaneous Wastes 141, 172 181 331 512 513 541 SS1 SIC S7 • Total 242.5 r 1 LJ 3-61 80.79 20.97 18.75 8.73 27.50 77.93 354.37 51.13 52.23 4.02 14.46 0.19 711.09 234.60 2.12 28.33 266.66 29.18 24.80 30.35 48.03 62.60 56.10 20.81 1.09 806.67 Table J Waste Group Waste Managed Oncite SIC CODE: S8 - Instrumeats.and Related products Waste Managed Offaite 1986 (1) 1967 (1) Tons Tons Waste Oil 15.84 Halogenated Solvents 7 ~ Non-Halogenated Solvents 2.70 Oily Sludges 322 Dye B. Paint S]udges 8 Resins 1.37 Non-metallic Inorganic Liquids tion•metallie Inorganic Sludges 9iscellaneous Wastet 172 181 331 0.61 512 0.44 551 0.21 SIC 38 • Total 31.45 SIC CODE: 39 •MiscxIIaneouc Manttt`acturiag Iaductries Halogenated Solvents '~`"" ""%' ~ Non-Halogenated Solvents 5.40 ~~ '~~' Miscellaneous Wastes ~ ~~ ,~:; 541 83.40 r~~.. ~:~:'~208aLI' SIC 39 • Total 88.80 214.31 SIC CODE: 40 -Railroad Transportation ~i"aste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids 1,680.0 Oily Sludges 3,633.0 Halogenated Organic Sludges Miscellaneous Wastes 181 . SIC 40 • Total 5,513.0 855.38 ~ 42.21 . ~ ~~~ ~' ~9 ~ " ` b b . 1 ~ y n , `~M~L ' "~k: 2,395.75 :8 } t~° ..'. ~~'383~6. 187.06 ~N~=~~.~ ~,~~~. 52.24 ~~6 3,532.64 4,273.80 SIC CODE: 41-Local and Interurbaa Passenger Transit Oily Sludges 14.59 ~~: ~~• X18:; Non-Halogenated Organic Sludges 4.78 ~::.: .:~~~' SIC 41 • Total 19.37 16.68 Table J • • ?•6?. Table J • Waste Group Waste Managed Onsite SIC CODE: 42 -Trucking and Warebouciag Waste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids Oily Sludges Non-Ha]ogenated Organic Sludges Dye 8 Paint Sludges & Resins Meta]-Containing Liquids Metal-Containing Sludges Non-metallic Inorganic Liquids Miscellaneous Wastes 141 181 512 551 SIC 42 • Total • SIC CODE: 43 • U. S. Postal Service Non•Halogenated Solvents SIC 43 • Total SIC CODE: 45 • Transportation by air Waste Oil Halogenated So]vents SIC 45 • Total SIC CODE: 48 • Communications Waste Oi] Non-Halogenated Solvents Organic Liquids Oily Sludges Meta]•Containing Liquids Non-metallic Inorganic Liquids Misce]laneous Wastes • 331 SIC 48 • Total Waste Managed Offsite 1986 (1) 1967 (1) Tons Tons 1.9s 0.01 76.71 6.25 39.34 1.66 38.52 3.24 25.91 0.02 0.94 194.63 0.10 0.10 13.43 24.24 37.87 ,~22. 0.22 ~> ~.~' .............;- ~~. 5I ~'. 18.76 ~...,.. 8 ~~: ~°,gz.~'3~" s~'~. ~"3..s11 ~~~.; ir~~~,... °'. ~~ ~ . ~::.. e .. <;, ~$ 21.93 3-63 Waste Group Waste Managed Onsite Waste Managed Offsite 1986 (1) 1987 (1) Tons Tons SIC CODE: 49 • Electric, Gac, and Sanitary Service Waste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids Oily Sludges Halogenated Organic Sludges Non•Halogenated Organic Sludges Dye 8 Paint Sludges 8. Resins A4eta1•Containing Liquids Afetal-Containing Sludges Non-metallic Inorganic Liquids Aliscellaneous Wastes 141 162 181 331 491 512 513 SIC 49 • Total 154.16 0.66 16.47 0.64 286.34 0.25 107.69 0.27 0.49 1.68 0.35 22.12 47.13 0.47 10.46 0.21 64858 SIC CODE: 50 • Wholesale Trade -Durable Goods «`aste Oil 0.22 , 'u,~ ~a 59. Non-Halogenated So)ventc a~ ~ a ~).I13' .:R~~~~~..' Oily Sludges ...~~1 SIC 50 • Total 0.22 3553 SIC CODE: 51 -Wholesale Trade • Nondurable Goods ~i'aste Oil 3.31 Non•Halogenated Solvents 15.84 Organic Liquids Oily Sludges Halogenated Organic Sludges A'on-Halogenated Organic Sludges 13.34 Metal-Containing Liquids 8.34 Non-metallic Inorganic Liquids 5.47 SIC bl • Total 46.30 ~~~~~ ~~ ~~ -a~~~ X18: ~"' ~~~.: :: :.:.:. Sb.81 Table J i • 1. 3-64 Table J • Waste Group Waste Managed Waste Managed Offsite Onsite 1966 (1) 1967 (1) Tons Tons SIC CODE: 52 • Building Materials and Garden Supplies Waste Oi] 0.29 Non-Halogenated Solvents 0.41 0.42' Dye & Paint Sludges & Resins ___ _,.. -0:88: SIC 52 • Total 0.70 1.30 SIC CODE: 5S • General Merchandise Stores Non-Halogenated Organic Sludges ' .~ 0.53 Miscellaneous Wastes 141 ~ x:13., 331 `'138` SIC 53 • Total 4.14 SIC CODE: 55 • Automotive Dealers and Service Stations Waste Oil 31.62 ~".$9.'l7 Non•Halogenated Solvents • 2.92 , ; x.`355: Organic Liquids 7.46 a ~ ';k~.0.'75 Oily Sludges 1.47 '' `~~~~3.'96 Halogenated Organic Sludges r~t > Non•Halogenated Organic Sludges ""`a37 a':x Dye 8 Paint Sludges & Resins 6.03 y ` ~4t~3' SIC 55 -Total 4952 84.63 SIC CODE: 72 • Personal Services Halogenated Solvents 0.13 ~'~< ~b88.' Non•Halogenated Solvents 3.74 SIC 72 • Total 3.67 15.68 SIC CODE: 73 -Business Services Oily Sludges 0.21 Non-Halogeneated Organic Sludges 0.91 Miscellaneous Wastes 331 ~"`~~~ 511 z°~:~,~>x~,;~< °' a 3>z u> < 541 y ~' • SIC 7S • ToffiI 1.12 156 3-65 Waste Group Waste Managed Onsite Waste Managed Offsite 1986 (1) 1967 (1) Tons Tons SIC CODE: 75 • Auto Repair Services and Parking Waste Oil Non•Halogenated Solvents Oily Sludges Non-Halogenated Organic Sludges Dye 8. Paint Sludges & Resins Metal-Containing Sludges :~4iscellaneous Wastes 181 SIC 75 -Total 78.94 12.63 4.07 95.64 :5523 >. ,~>16.81 ..*....>3:9~7:. ~:,;:,;.~67 s ..2:~$. ~~ f ... ~~'16.84 128.07 SIC CODE: 76 -Miscellaneous Repair Services Non•Halogenated Solvents Dye b Paint Sludges & Resins Metal-Containing Liquids Non-metallic Inorganic Liquids Tiiscellaneous Wastes 512 513 SIC 76 -Total SIC CODE: 79 -Amusement & recreation Services Waste Oil Oily Sludges Non-Halogenated Organic Sludges SIC 79 -Total Table J 4.40 3.37 4.00 k" .1:20 - ~ 1.00 °°a xa~`'' 14.70 4S7 , SIC CODE: BO -Health Services Waste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids Oily Sludges Dye g Paint Sludges & Resins 1.Iiscellaneous Wastes 141 181 322 331 512 513 b51 SIC 80 • Total 4.62 0.42 0.84 0.16 0.21 2.85 1.47 0.63 0:11 0.02 3.45 14.78 :13:'34 --_ .:;::.x:92 47.32 3-66 • Wastc Croup Waste Managed Onsite SIC CODE: 82 -Educational Services u Waste Managed Offsite 1986 (1) 1967 (1) Tons Tons Waste Oil Halogenated Solvents Non•Halogenated Solvents Organic Liquids Oily Sludges Non•Halogenated Organic Sludges 1.70 Miscellaneous Wastes 181 1.68 512 513 551 7.03 SIC 82 -Total 10.41 SIC CODE: 87 -Engineering & Management Servicec Waste Oi] • Metal-Containing Liquids 0.9 SIC 87 -Total 0.9 SIC CODE: 91 • Executive, Legiciative & General 0.60 Waste Oil 0.22 k-~'...~.64 Halogenated Solvents 0.20 x.:;.0.10 Non-Halogenated Solvents 1:$1 Oiiy Sludges ~'t4;$1` :. Non-Halogenated Organic Sludges , • -5:2? Dye S Paint Sludges & Resins , A:41'' Aiscellaneous Wastes ,~ ~ := 491 ~ 'Z'2:31 SIC 91 • Total 0.42 b2.35 SIC CODE: 92 • Justice, Public Order & Safety Organic Liquids ~ 'K 959: Oily Sludges s~,~~ b.~,,,0~3i Miscellaneous Wastes n n ~:E~ ~ ~! 141 ~s*x~ x.26`; 331 <:~•a~.~~:~t1i 512 9 a~"~~~ 00? • SIC 92 -Total . 14 79 Table J 3-67 Waste Group Waste Managed Waste Managed Offsite Onsite 1986 (1) 1987 (1) Tons Tons SIC CODE: 97 • National Security & International Affairs Waste Oil 2.8 482.60 Halogenated Solvents 10.94 Non-Halogenated Solvents 7.90 Organic Liquidc 131.19 Oily Sludges 346.67 halogenated Organic 5ludgea 2.55 Non-Halogenated Organic Sludges Dye 8. Paint Sludges & Resins 5.61 Metal-Containing Liquids 2.34 Non-metallic Inorganic Liquidc 10.24 A'fiscellaneous Wastes 141 11.41 181 26.25 331 5.69 491 511 512 240.54 513 541 4.6 55:21 551 14.26 612 SIC 87 • Total 7.4 1,355.40 SIC CODE: Unlmowa Vvaste Oi] 9,742.17 Halogenated Solvents 32.62 Non-Halogenated Solvents 662.90 Organic Liquids Oily Sludges 10.94 Dye & Paint Sludges & Resins Metal-Containing Liquidc 7.43 Metal-Containing Sludges 12.64 Miscellaneous Wastes 181 8.51 612 19.12 SIC Unlmowa -Total 10,496.33 Table J • • 3-68 Waste Group Waste Managed Onsite Table J -Totals for each Waste Group Waste Managed Ofisite 1986 (1) 1987 (1) Tons Tons Waste oil 2.8 12,594.25 Halogenated solvents 139.57 Non-halogenated solvents 2,741.27 Organic liquids 554,698.7 187.33 Oily sludges 3,633.0 3,837.78 Halogenated organic sludges 169.86 Non-halogenated organic sludges 188.25 Dye g Paint sludges 2.1 294.58 Metal containing liquids 614,776.5 22,937.30 hfetal containing sludges 293.0 540.20 Non-metallic inorganic liquids 258,22 Non-metallic inorganic sludges 52,23 Miscellaneous 141 Off-spee.inorganie 13.29 _151 Asbestos 162 Other spent catalyst 22.12 172 Meta] dust 58.10 181 Otherinorg.soiid waste 143.0 1,267.47 322 Biological waste 1.47 331 Off-epee. organics 18.51 491 Unspecified cludge 297.03 511 Empty pesticide eont.>30 gal 0.00 512 Other empty containers>30 gal 990.68 513 Empty containers < 30 gal 15.06 541 Photochemical waste 4.6 138.61 551 Laboratory waste 27.69 561 Detergent & soap 23.59 591 Baghouse waste 5,751.89 612 Household waste 19.12 subtotal 147.6 8,144.53 Total wastes ~ 1,173,903.3 52,105.37 (1) The data for this Table was taken from the California Department of Health Services Hazardous Waste Information System database, corrected as diseuesed in previous Tables and supplemented with information from San Bernardino County Department of Environmental Health Services files for individual SIC codes. All wastes in the HVi'IS database, except cleanup wastes and wastes generated from the removal of underground tankc (as shown in Table I), are included. • (2) Route haul service wastes are listed with the unknown SIC Code since these wastes come from a variety of SIC codes. Table J o_ao u 3.4.11 Table K Table K presents projections of hazardous waste generation levels in the year 2000 by major industrial groups for wastes managed both on-site end offsite. Tbese projections are based on the average of the 1986 and 1987 routine hazardous waste generation levels as shown in Table J, plus the estimate of existing small quantity generator wastes not captured by the regulatory program, shown in Table I. The estimated small quantity generator wastes identified in Table I were not separated by industrial category. Rather, they are included in the aeetion for "unknown" SIC code. The bulk of small quantity generator categories identified in the estimate are service-related industries, although they include s range ofS1C codes. These projections assume that all wastes currently managed on•site will continue to be managed on-site; and s11 wastes managed offsite will continue to be managed offsite, with one exception. The company which ships "metal containing liquid" via pipeline to Chemwest is currently developing process modifications which will enable it to recycle the hydrochloric acid and sell the ferrous chloride as product The projections reflect the fact that these wastes will no longer be generated. The growth factor shown for each major industry group is taken from the Draft Baseline Proiectionl. These projections provide estimates of the percent change in employment in each industrial category between the years 1984 and 2000. The projected change for each two digit SIC category is shown in Table K with the category. The projected changes range from a decrease of 6.996 for some categories to an increase of 35095 for the "transportation equipment" category. The large peroenb age change in employment for the "transportation equipment" category reflects both anticipated growth and the feet that this particular category is currently relatively small. Thus even a modest increase in absolute numbers yields a large percentage change. The use of 1984 to 2000 projections introduces some error into the calculations since the waste data are based on 1986 and 1967 levels. It should be rerngnized that these projections are attempting to describe cyclical economic activity in a linear manner. Thus, some error is introduced. Additionally, it is recognized that employment levels are not necessarily the best indication of waste production. Numerous attempts to obtain economic projections for this area by SIC code, including several calls to vnri- ous offices in the U.S. Department of Commerce, Bureau of Economic Analysis, the California Employment Development Department's Economic Data end Research Division, the California Department of Finance, the Southern California Association of Governments, as well as the county Economic Development Department and Office of Land Management were all unsuccessful. The employment growth projections used wen the only figures related to apecifie industrial sectors available. While employment levels provide some indication of waste generation, these are not the best indicators for projection purposes because they include non-production staff (sales, management, etc.). Production levels or income figures are more directly cor- related with waste generation, however, these figures are not generally available. It should also be noted that the use of primary 5IC code does not always describe the actual operation causing waste generation. For example, a food processing plant 1 Draft Baseline Proieetion: Subreeional Breakdown, Southern California Association of Governments, Los Angeles, 1986. • ~~ • 3-70 which also manufactures and coats its own cans produces different wastes than one who purchases cans. Ideally, the manufacture and coating of the can would be identified as a secondary SIC code. The growth factor used for the "unknown" SIC code is based on the population projee• tions developed by Southern California Association of Governments and published in the same report identified above. Since most of the wastes included in the "un• known" section are waste oil, lead acid batteries, and since the small quantity gener• ators are for the most part service-related, apopulation-based projection seemed most appropriate. As can be seen from these projections, it is expected that almost 70,000 tons of haz- ardous waste will be generated and shipped offsite in San Bernardino County in the year 2000 if there is no effort to reduce the level of hazardous waste generation. The significant impact of the process change at one company as described above under- scores the importance of promoting waste minimization efforts in the future. Figures K-1 and K-2 summarize and illustrate these data. Wastes shipped offsite are projected to be dominated by the "unknown" rategory which includes both route hauler wastes and the SQG planning estimate. This underscores the importance of existing Department of Environmental Health Services programs for generators which are described in Chapter 7. • Figure B•1. Projected Industrial Sources of Hazardous Waste Managed Otfsite (2000) Unknown Primary metal industries Utilities - Railroad transportation - 2~anaportation equipment - Mise. ~ National security Fabricated metal products Non-metallic minerals Chemieals&allied prod. 5000 10000 15000 Tons 20000 25000 30000 3.71 Primary metal industries Fabricated metal products Railrwd transportation Eleotronie equipment Metal mining T~ansoortation equipment Misc. Ioo Iooo Ioooo Iooooo Ioooooo Iooooo00 Tons (I.ogarithmie scale) • 3-72 Figure K-2. Projected Industrial Sources of Hazardous Wastes Managed On-cite (2000). • TABLE K -PROJECTED QUANTITIES OF HAZARDOUS WASTE BY MAJOR IIQDUSTRY GROUPS (2000) SIC CODE: 10 -Metal Miaiag Growth factor. 096 Waste Group Waste Managed Onsite 1986 (1) Projected (2) Tons Tons/year SIC CODE: 14 -Non-Metallic Minerals, ezcept fuels Growth factor. 096 ~'aste Oi] halogenated Solvents Non-Halogenated Solventc Organic Liquids Oily Sludges Dye b Paint Sludges & Resins Non-metallic Inorganic Liquids Miscellaneous Wastes 141 161 143.0 331 512 513 551 591 SIC 14 -Total 143.0 Table K Waste Managed Oftsite Planning Projected (2) Estimate (3) Tons/year Tons/year 164.26 0.40 576.07 11.67 310.89 0.25 0.52 6.45 22.17 3.23 102.71 0.64 0.52 12.46 1,234.22 .............. . 7.fi4 26:62 34.46 SIC CODE: 16 -Heavy Construction, excluding Building Growth factor. 73.796 «'aste Oil 1.87 .s~' ` ~~~.25` Non-Halogenated Solvents 14.80 e , ~.' ~ ~,~. Oily Sludges U•84 ~ ~ ~"`~~'~I' •Iiscellaneous Wastes a xr '` ```" ~• 512 1.93 ,,,.~'...... a :x.34 - SIC 16 -Total 19.'41 33.78 3-T3 ' Tabie K Waste Group Waste Managed Onsite Waste Managed Offsite 1986 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 17 • Special Trade Contractors Growth factor. ?3.7^6 Waste Oil 4.17 Halogenated Solvents 0.19 Non-Halogenated Solvents 20.37 Organic Liquids 1.49 Oily Sludges 2,06 Dye & Paint S]udges & Resins 3.29 Non-metallic Inorganic Liquids 0.42 Miscellaneous Wastes 181 0.08 331 1.46 512 1.02 551 p,p4 SIC I7 • Total gq,5g SIC CODE: 20 • Food and Siadred Products Growth factor. 32.09'0 Non-Halogenated Solvents 10 01 ~ %'"13~] Dye 8 Paint Sludges 8 Resins . 0.19 ' p v< SDI{ Miscellaneous Wastes >;, ~im~"~~~~9F' ` ~~ ~ R My'~~)~~,.f. ': 551 0.95 ~::.°..::~:i.:: SIC 20 -Total 11.14 ~y 14.70 SIC CODE: 24 • Lumber and Wood Products Waste Oil Non-Halogenated Solvents Oily Sludges Dye & Paint Sludges 8 Resins Aleta]-Containing Sludges SIC 24 • Total Growth factor. 19.4Ro 6.21 L26 6.59 2.51 6.31 22.88 SIC CODE: 25 • Furniture and Fixtures Growth factor. -8.996 Halogenated Solvents Non-Halogenated Solvents Oily Sludges Dye ~ Paint Sludges & Resins Metal-Containing Liquids SIC 25 -Total s 711 ~U 3~ ~ 27.31 L52 ~„~.nM:r ~ 4.49 A ~:~s"'fl9 Y L41 ~~,,,,F....: in„ `:.;:.. u`,kc ;B 0.42 : ,~$! 9.38 ~_:.,;:.:, ...... 17.22 Ib.69 • • ~~ • 3-74 • Table K Waste Group Waste Managed Onsite Waste Managed Offsite 1986 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 26 -Paper and aIIied products Growth factor. 64.996 Waste Oil Non•Halogennted Solvents Organic Liquids Oily Sludges Dye & Paint Sludges & Resins Miscellaneous Wastes 331 SIC 26 • Total 51.29 214.71 13 97 16.99 30 02 1.49 328.46 SIC CODE: 27 • Printing and Publishing Growth factor. -8.990 t4 aste Oil lion-Halogenated Solvents Oily Sludges lion-Halogenated Organic Sludges ve & Paint Sludges & Resins 4iseellaneous Wastes 181 331 491 SIC 27 • Total 6.59 103.46 0.57 8.34 2.00 0.11 0.21 0.46 121.70 SIC CODE: 28 -Chemicals and allied Products Growth factor. -8.990 «'aste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids Oily Sludges Non-Halogenated Organic Sludges Dye g Paint Sludges 8 Resins Metal-Containing Liquids Nonmetallic Inorganic Liquids Miscellaneous Wastes 181 491 512 • 513 551 SIC 28 • Total 1.7 1.9 3-75 0.89 2.83 467.47 0.66 8.64 0.42 64.94 1.5 0.10 433.85 42.81 80.87 4.25 0.25 1,108.18 x :84:K7 _ _.._ . 35+L'06 ..., 23U3 ,:.28OT. 49.50 ":2:#S 541.62 •~iTfO :94:25 :x.39, tlltt ' X1:39 ~""" .s=11 ~~' 110.87 Table K Waste Group Waste Managed Onsite Waste Managed Offsite 1986 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 28 -Petroleum sad Coal Products Growth factor. -8.996 Waste Oi] 59.76 84.44 Non-Halo mated Or nie Slu g ga dges 6.13 ~, ~7 41 Miscellaneous Wastes " ~~ ° 161 6.28 ~> ~ $~2 SIC 28 -Total 74.17 67.56 SIC CODE: SO -Rubber cad Misc. Plastics Products Growth factor. -8.896 Waste Oil Halogenated Solvents Non-Halogenated Solvents Oily Sludges Dye g Paint Sludges & Resins Non-metallic Inorganic Liquids Aliseellaneous Waster 491 SIC 30 -Total • 29.89 2?~$ ~ 1.63 ~ W %;146 12.73 ..:.: _... "1L59 4.27 8.89 : 87 5. ::.. x:. :.::.....:..: z 5: 3± [ } / U.25 ~ q M A ~h " AI.W ~~ ~ F> ~ 0 18 '~ ~~< . 54.60 48.82 • ;, SIC CODE: S2 - Stoae, Clay and Glass Products Growth factor. 11.496 ~L'aste Oil Halogenated Solvents Non•Halogenated So]vents Organic Liquids Oily Sludges Dye 8 Paint Sludges & Resins Non-metallic Inorganic Liquids Miscellaneous Wastes 491 512 551 SIC S2 -Total SIC CODE: SS • Primary Metal Industries 1Vaste Oil Halogenated Solvents Non•Halogenated Solvents Organic Liquids Oily Sludges Metal-Containing Liquids 536,010.0 606,692.0 7a.s1 0.14 1.97 2.29 0.53 10.11 1.56 5.21 2.22 0.04 98.86 Growth factor. 52.496 3-76 49.79 L81 13.13 2.92 0.30 • • Waste Group Metal•Containing Sludges Non-metallic Inorganic Liquids Miscellaneous Wastes 181 561 591 SIC 33 -Total SIC CODE: 34 • Fabricated Metal Products Waste Oil Halogenated Solvents ?:on-Halogenated Solvents Organic Liquids Oily Sludges Non-Halogenated Organic Sludgec Dye & Paint Sludges & Resins ~tal-Containing Liquids tal-Containing Sludges on-metallic Inorganic Liquids Miscellaneous Wastes 141 172 181 491 512 551 SIC 34 • Total Table K Waste Managed Onsite 1986 (1) Projected (2) 1,144,702. Waste Managed Offsile Planning Projected (2) Estimate (3) 100.26 ,._.''152:79 64 15 ' .97:76 69.98 M e~ .106:6 35 BO ~ 64515 6.061.21 _ :9,237:28 6,399.32 8,752.b6 Growth factor. 39.596 15,000.0 440.0 15,440.0 121.50 13.97 24.91 73.74 16.66 59.72 1.38 0.11 126.37 191.84 O.B5 1.03 1,365.88 SIC CODE: 35 • Industrial Machinery and Equipment Growth factor. 20.096 ~T.'aste Oil 1.79 ?von-Halogenated Solvents 31.46 Oily Sludges 7.30 Dye 8 Paint Sludges & Resins 30.52 Metal-Containing Liquids 17.30 Non-metallic Inorganic Liquids 24.93 A4isee]laneous Wastes 141 0.08 512 3.00 • 513 0.11 SIC 35 • ToffiI 116.47 380.61 15.39 357.83 3-77 21538.8 1,933.30 Table K Waste Group Waste Managed Oncite Waste Managed Offsite 1986 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 36 -Electronic sad other Electric Equipment Growth factor. 26.396 Waste Oil Halogenated Solvents Non-Halogenated Solvents Oily Sludges Halogenated Organic Sludgec Dye & Paint Sludges & Resins 2.1 lv2eta]-Containing Liquids 5,210.1 Metal-Containing Sludges Non-metallic Inorganic Liquids Non-metallic Inorganic Sludges Miscellaneous Wastes 172 181 491 512 551 SIC 38 • Total 5,222.2 SIC CODE: S7 -Transportation Equipment R'aste Oil Halogenated Solvents Non-Halogenated Solvems Organic Liquids 8.7 Oily Sludges Non-Halogenated Organic S}udges Dye g Paint Sludges & Resins Metal-Containing Liquids 233.6 Meca1-Containing Sludgec Non-metallic Inorganic Liquids Miscellaneous Wastes 141 172 181 331 512 513 641 551 SIC 37 • Total 42.77 10.88 18.68 4.3? 0.56 13.7b 58.79 391.35 34.63 39.60 10.15 15.07 7.24 5.48 0.10 'W~:: Growth factor. 350.090 186.41 13.02 35.40 0.99 227.64 25.60 28.83 15.70 133.35 68.9? 0.32 37.89 21.34 2.10 2.10 94.80 0.42 1.47 696.33 • • 3-78 • Table K Waste Group Waste Managed Oncite Waste Managed Of3site 1986 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 38 • Instruments and Related Products Growth factor. -8.9Ao Waste Oil 8.70 `: 7:92. Halogenated Solvents 5.41 4HS ~. Non-Halogenated Solvents 2.31 ~ ° 230' Oily Sludges 15.20 , . ^13:54 Dye & Paint Sludges & Resins 0.69 " •fi2 D. Non-meffi]]ic Inorganic Liquids 0.16 , ..'13.14 Non-metallic Inorganic Sludges 0.16 ~Oa4 Miscellaneous Wastes ,. . 172 10.54 181 0.56 331 1.04 512 0.22 551 0.11 SIC 38 • Total 45.06 5IC CODE: 39 -Miscellaneous Manufacturing Industries . Growth factor. •8 896 Halogenated Solvents 0.10 < p.09 Non•Halogenated Solvents 6.55 ~, ,;~;:~,97 AlisceAaneous Wastes ~ .:s ~::~;,.:,,,t` 541 144.91 132.'01 SIC 39 • Total 151b6 138.07 SIC CODE: 40 • Railroad Transportation Growth factor.78.296 Waste Oil 1,150.64 >2i1b0:#3 Halogenated Solvents 25.28 ?45:D4 ?von-Halogenated Solvents 1.25 ~ 2:12 Organic Liquids 1,680 0 ~°"~,1593~' Oily Sludges 3,833.0 ~:~"~~~~830.4' 2,589.56 +1,6i4~9 Halogenated Organic Sludges ~~;#~ D~~.ve kµ„~~ ~, ~~ 106.16 T8918 Miscellaneous Wastes a~~ ~ '. 181 ~.~m~"'.vm...i 30.25 '33.91 SIC 40 • Total b,513.0 9624.2 3,903.12 6,955.36 SIC CODE: 41 • Lord and Interurban Passenger Transit Growth factor. 78.296 ilv Sludges 15.64 ~' ~7 BB ~on-Halogenated Organic Sludges 2.39 a a~~4:26' SIC 41 • Total 18.03 32.12 3-79 Table K Wasu Group Wasu Managed Onsite Waste Managed Offsiu 1996 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 42 -Trucking and Warehousing Growth factor. 78.296 Waste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids Oily Sludges Non-Halogenated Organic Sludges Dye g Paint Sludges & Resins Metal-Containing Liquids Metal-Containing Sludges Non-metallic Inorganic Liquids Miscellaneous Wastes 141 181 512 b51 SIC 42 -Total SIC CODE: 43 • U. S. Postal Service Non-Halogenated Solvents SIC 43 • Total 2.02 0.33 63.72 3.13 32.54 0.64 31.40 1.60 0.42 1.75 3.06 38.28 0.11 0.47 178.63 0.11 ~~;>,~{j'. ..... ...... 0.11 0.20 SIC CODE: 45 -Transportation by air Growth factor. 78.296 Wasu Oi] 0.63 ~"~`, '~3 Halogenaud Solvents 8.76 ~ <~'~~i60 SIC 45 -Total 9.38 16.72 SIC CODE: 48 - Commnaicationc Growth factor. lO1.S96 Wasu Oi] L30 ~~_~E2 Non-Halogenated Solvent 0.73 ~" Organic Liquids 8.46 ~D2; Oily Sludges 0.13 ,nil;2$ Metal-Containing Liquids 6.7b x; °' i Non-metallic Inorganic Liquids 12.15 ' Discellaneous Wastes ~; - >. 331 0.39 ~;,;_: _ SIC 48 • Total 29.90 60.19 Groevth factor. 78.296 .. 3-80 • Table K Waste Group Waste Managed Onsite Waste Managed Offsite 1986 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 48 • Electric, Gas, and Sanitary Service Growth factor. 101.390 waste oil 192.72 Halogenated Solvents 0.36 Non-Halogenated Solvents 23.36 Organic Liquids ~ 0.66 Oily Sludges 146.53 Ha]ogenated Organic Sludges 0.13 Non-Halogenated Organic Sludges 65.44 Dye 8 Paint Sludges & Resins 1.16 Metal-Containing Liquids 93.48 metal-Containing Sludges 12,fi4 Non-metallic Inorganic Liquids 35.48 I`4isce1laneous Wastes 141 5.66 lsz ll.os 181 108.00 331 5.29 491 2,639.06 • 512 10.77 513 0.21 SIC 49 -Total 3,551.97 SIC CODE: 50 • Wholesale Trade -Durable Goods Growth factor. 60.790 Waste Oil 12.91 20.74 Non-Halogenated Solvents 0 02 €D.02 Oih• Sludges 496 = '?_~6 SIC 50 -Total 17.88 28.73 SIC CODE: 51 -Wholesale Trade -Nondurable Goodc Growth factor. 60.7% K'aste Oi] 5.18 °. 8.32 Non-Halogenated Solvents 896 ,,, <s , 14.40 Organic Liquids 3.13 , `S.t12: Oily Sludges 10.22 ~,~~ lb 42' Halogenated Organic Sludges ~ rx ~~ Non-Halogenated Organic Sludges 6.67 M10:72, , 1vSetal-Containing Liquids 4.17 ... ~7 „::` ~'a1). 1Qon•metallie Inorganic Liquids 2.74 ~ ~ ~ 4~0 ~~ • SIC 51 • Total 41.06 65.98 3.81 • Table K Waste Group Waste Managed Onsite Waste Managed Oftsite 1986 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 52 -Building Materials and Garden Supplies Growth factor. 78.396 Waste Oil 0.15 ......:. .._;;:_ :036 Non-Halogenated Solvents 0.42 ,~~' ~ fl:7# Dye & Paint Sludges & Re:ins 0.44 ~,<;;.;.;;.,.`,.;=07$ SIC 52 • Total 1.00 1.78 SIC CODE: 53 • General Merchandise Stores Growth factor. 78.396 Non-Halogenated Organic Sludges 0.27 1v4iscellaneous Wastes 141 1.22 331 0.59 SIC 53 • Total 2.07 SIC CODE: 55 • Automotive Dealers and Service Stations Growth factor. 78.396 Waste Oil Non•Halogenated Solvents Organic Liquids Oily Sludges Halogenated Organic Sludges Non-Halogenated Organic Sludges Dye 8 Paint Sludges ds Resins SIC 55 -Total SIC CODE: 72 • Personal Services Growth factor. 80.696 Ha)ogenated 5o]vents Non-Halogenated Solvents SIC T2 • Total SIC CODE: 7S • Business Services Oily Sludges Non-Halogeneated Organic Sludges Miscellaneous Wastes 331 Sll 541 SIC 73 -Total Growth factor. 122.196 3-R2 35.45 8.29 9.22 6.62 2.59 5.03 67.06 3.69 119.59 ~µ~'~4~8 7.91 ~x ~ 1.67 ~ ~'. B28 8.78 17.65 0.11 0.46 0.32 ~~', "73 023 ~` ~ ~' o.u 1.35 3.00 • • ,, ~. • Table K Waste Group Waste Managed Onsite Waste Managed OfTsite 1986 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 75 • Auto Repair Servicec and Parking Growth factor. 75.696 ... . . . Non-Halogenated So]vents 14 72 ... .. . .... ~~ ..... 25:65 Oily Sludges 14 59 2fii~i Non-Halogenated Organic Sludges 334 4'86 Dye 8 Paint Sludges & Resins 328 ~~`~ 5:7b Meta]-Containing Sludges 044 A:76 Miscellaneous Wastes ~ 181 8 42 . a4:?9 SIC 75 • Total 111.86 196.42 5IC CODE: 76 • Miscellaneous Repair Services Growth factor. 75.696 ton-Halogenated Solvents 2.20 3.66 Dye € Paint Sludges & Resins 169 2.>36 Metal-Containing Liquids 2.00 ~:bl Non-metallic Inorganic Liquids 0 60 '1'DS 3scellaneous Wastes 512 0 50 •x:86 513 2.65 `•._ _ _ ,..:.4:66 SIC 76 • Total 9.64 16.92 SIC CODE: 79 -Amusement 8 recreation Servicec Growth factor.B2.896 Waste Oil 13 03 X3.82 Oi}y Sludges 6 67 '2:9 Non=Halogenated Organic Sludges 3.96 7~4 SIC 79 • Total 23.66 43.25 SIC CODE: 80 -Health Services Growth factor.120.34c «'aste Oi] 1.07 Halogenated Solvents 0.15 Non-Halogenated Solvents 3.46 Organic Liquids 1.55 Oily Sludges O.B4 Dye 8 Paint Sludges & Resins 0.61 Miscellaneous Wastes 141 0.11 181 2.37 322 0.74 331 0.53 • 512 0.06 513 0.01 551 3.71 SIC 80 -Total 15.17 3-63 u Table K Waste Group Waste Managed Onsite 1986 (1) 1'rojeeted (2) SIC CODE: 82 -Educational Servioes Growth factor32.896 Waste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids Oily Sludges Non-Halogenated Organic Sludges Miscellaneous Wastee 181 512 513 551 SIC 82 -Total Waste Managed Offsite Planning Projected (2) Estimate (3) 0.05 0.03 9.43 0.11 0.26 LO6 1.36 2.38 0.01 5.67 20.35 • SIC CODE: 87 -Engineering & Management Services Growth factor. 82.8'k Waste Oi] 0.30 0.55 Metal-Containing Liquids 0 9 ~ p1.~' '~~ ' ~ SIC 87 -Total ~ 0.9 1.6 030 OS5 SIC CODE: 91 -Executive, Legislative & General Growth factor. 40.296 Waste Oil Halogenated Solvents :ion-Fislogenated,Solvents Oily Sludges ?: on-Halogenated Organic Sludges Dye & Paint Sludges & Resins Miscellaneous Wastes 491 SIC 91 -Total 1.66 ~u.:s:,:::_:;<<~,~t4 0.15 : ~ ~ 0.91' >, » ,r. 'L27 12.41 r ,~~ a >~ ti~.~~9. 4.59 ~ .~ x.443. 0.21 .~ 9 ~~ ~M~:: 6.26 ~ "`,~'~ S:TJ 2639 36.99 SIC CODE: 82 • Juctix, Public Order & Safety Growth factor. 40.296 Organic Liquids 4.80 Oily Sludges 0.23 Miscellaneous Wastes 141 331 512 SIC 82 • Total 0.13 ~ ~`~` dl'I8 1.25 s~"~$ 1.00 ~~,~:~;s~~ ~4 ?.40 103? • • 3-64 • Table K Waste Group Waste Managed Onsite Waste Managed Offsite 1986 (1) Projected (2) Planning Projected (2) Estimate (3) SIC CODE: 97 • National Security & International Affairs Growth factor. 40.296 Waste Oil ~ 2 8 Halogenated Solvents Non-Halogenated Solvents Organic Liquids Oily Sludges Halogenated Organic Sludges ?von-Halogenated Organic Sludges Dye 8 Paint Sludges & Resins Meta]-Contairring Liquids Non-metallic Inorganic Liquids Miscellaneous Wastes • 141 181 331 491 511 512 513 541 4.6 551 612 SIC 97 • Total 7.4 SIC CODE: Unknown Growth factor. 23.996 (2> 1~'aste Oil Halogenated Solvents Non-Halogenated Solvents Organic Liquids Pesticides Oily Sludges Halogenated Organic Sludges Dye b Paint Sludges & Resins Meta]-Containing Liquids Af etal-Containing Sludges Non-metallic Inorganic Liquids Non-metallic Inorganic Sludges Miscellaneous Wastes 181 • 511 541 612 SIC Unknown • Total 598.25 18.67 175.76 121.78 337.62 1.28 0.34 7.46 9.65 7.65 6.57 28.65 8.50 66.88 0.03 173.24 31.90 29.53 7.50 0.02 9.20 40:17 1,633.65 18,222.49 50.46 1,507.93 85.53 145.76 61.84 136.11 33.45 2,705.80 6.71 205.86 3.15 232.71 70.15 130.60 18.62 23,619.34 3-B5 10.5 29,264.36 n V,'aste Group Waste Managed Onsite 1986 (1) Projected (2) Table K - Totalc for each Waste Group Waste oil Halogenated solvents Non-halogenated solvents Organic liquids Pesticides Oily s)udges Halogenated organic sludges Non•halogenated organic c]udges Dye & paint sludges Aletalcontaining liquids Metal containing sludges Non-metallic inorganic liquids Non-metallic inorganic sludges Aiiscellaneous 141 Off-spec, inorganic 162 Other spent catalyst 172 Meta] dust 181 Other inorg. colid waste 322 Biologies] waste 331 Off-spec. organics 491 Unspecified sludge 511 Empty pesticide cont.>30 gal 512 Other empty eontainers>30 gal 513 Empty containers < 30 gal 541 Photochemical waste 551 laboratory waste 561 Deurgent & soap 591 Baghouse waste 612 Household waste Total 2.8 554,698.7 3,633.0 2.1 614,?78.5 293.0 143.0 4.6 1,173,755.7 Table K Waste Managed Otfsite Planning Projected (2) Estimate (3) 21,402.60 165.38 3,717.76 272.22 145.76 3,970.19 246.50 146.36 302.98 2,996.35 668.13 521.60 42.75 .BS 24.94 11.06 56.66 1,166.35 0.74 26.39 3,167.48 70.41 368.42 134.57 305.70 21.84 35.95 6,073.69 18.64 46,107.8 • 3-66 • Notes on Table K (1) Data Sources The data were taken from Table J -Industrial Sources of Hazardous Wastes and the SQG estimate of Table I. The SQG estimate was included with the "unknown" SIC code wastes because apopulation-based projection factor is more appropriate for these service-related industries. (2) Growth Factors Growth factors for each major industrial group were taken from the Draft Baseline Proiection: Subreeional Breakdown, Southern California Association of Govern- ments, Los Angeles, 1986. The growth factors represent estimates of the percent change in employment in each industrial category between the years 1984 and 2000. The growth factor used for the "Unknown" 51C code is based on Southern California Association of Governments population projections, taken from the same report A~- cording to this projection, San Bernardino County will have a population of 1,536,600 in 20D0. This is compared to a current (1/1/68) population of 1,239,967 according to the Population Research Unit, California Department of Finance. (3) Planning Estimate For each major industry group, an average of the 1986 and 1987 hazardous waste generation levels shown in Table J was used. The estimated 5QG levels of Table I were added to the average of the 1986 and 1987 generation levels for SIC code "un- • known" in Table J to obtain the values shown. (4) Other Assumptions The Metal-containing inorganic liquids currently being shipped to Chemwest In- dustries for reryeling will be managed on=cite by the generator. Because portions will be recycled within the manufacturing process and the remainder sold as product, it is no longer classified as 8 waste. These projections assume all other wastes currently being shipped offsite for treat- ment, will continue to be shipped offsite, and wastes currently managed on-site will continue to be treated on-site. • 3-87 ~ i Table L Table L provides an estimate of the hazardous wastes projected to result from the clean up of contaminated cites, including underground storage tanks, old disposal sites, closed toxic pits and other clean up wastes. The estimate of wastes from un- derground tank removals is based on the data reported in Table I for 1987. Because only 4040 of the known tank removala actually used a manifest, the 1987 figures were multiplied by 2.5 to obtain the number of tonsyear for this estimate. Unfortunately, only very sketchy data is available at this time for the other categories of clean up wastes. Table L provides an estimate of annual waste generation levels from clean ups dur- ing the planning period (1989.2000). It is expected that clean ups from un- dergrounds storage tanks and asbestos removal will be completed during the plan- ning period, creating ashort-term immediate need for treatment and disposal capac- ity. These figures are not included in the projected need for 2000. It is not known when the wastes in the "old disposal cite" eateFory will be cleaned up and those fig- ures are carried forward to the 2000 projections. 3.68 • ,~ i • r1 L_J • Table L Table L - PROJECTED QUAIVTTPIES OF CLEAN UP ACTIVITY WASTE Waste group Underground Old Disposal Closed Other Total Tanks (1) Sites (2) Toxic Pits (3) Cleanup Wastes (4) Waste oil Halogenated solvents Non-halgtd. solvents Organic liquids Oily sludges Non-halgtd. sludges Dye & paint sludges Metal-containing liquids Contaminated soil Miscellaneous wastes 151 Asbestos 161 Other inorg. waste 512 Empty cont.>30 gal Tons~year 1,478:48 0.63 306.78 332.85 1,105.73 875.15 1.50 3,278.23 2,609.33 230.68 7,610.20 38,864.31 Tonc/year 7,304.27 42.00 28,728.71 Tons/year Tons/yr Tons/year 1,476.48 0.83 306.78 332.85 1,105.73 8,179.42 1.50 42.00 32,006.94 1,411.60 1,411.60 2,809.33 230.68 1,411.60 47,906.11 Data Sources: (1) Based on data presented in Table I for 1967 only. Because only 4096 of actual tank removals used individual manifests, these figures wen multiplied by 2.5 to obtain an estimate of wastes generated by all tank removals. It is ezpeeted that tank removals will continue at this level until all of the old tanks have been removed, approximately five yearc. Subsequently the level will drop significantly. (2)Based on data provided by DHS in a memo. The figures include estimated cleanup wastes only from the I{aiser Steel and Issae Cohen sites, as these are the only available data at this time. A complete listing and status report of all sites in San Bernardino County currently listed on the Expenditure Plan for the Hazardous Substance Clean Up Bond Aet of 1984 is provided in Appendix G. The estimates shown here were developed according to DHS Guidelines and assume that clean up will occur over a ten year period. These figures reflect wastes ezpeeted to be generated during one year of the clean up. (3) 1v~o information available at thic time. (4) This is an estimate of asbestos wastes to be removed from school buildings in San Bernardino County annually over the next three years. 3-89 Table M This Table is intended to project quantities of waste which will require proper man- agement as a result of changes in regulation. The first category involves pretreat- ment sludges which will result from various industries' attempts to comply with Clean Water Act requirements. More stringent discharge requirements by publicly owned water treatment fadlities will force businesses to "pretreat" their waste water prior to discharge to sewers. Ii is antiripated that the "pretreatment sludges" gener• ated will require management as a hazardous waste. At this time, there are no data available on which to base an estimate of the wastes generated. There are severs) categories of "Other new wastes" which are being watched closely by San Bernardino County DEHS. According to a recent article by Alex R Cunning- ham, Chief Deputy Director, DHS Toxic Substances Control Division in the Califor- nia Fire Journal, DHS is working on developing a streamlined permit program for the following five categories of hazardous waste facility: (1) Underground tank cleaning/sa)vaging operations (2) Waste oil handlers (3) Drum reconditioners (4) Precious metal reryelera and (5) Soil and water contaminalSon associated with leaking underground tanks. n Once these facilities are fully permitted, all wastes handled by them will have to be managed as a hazardous waste. Estimates for underground tank removals (1 and 5 above) are provided in Table L Estimates for waste oil are covered in Table K At the present time there is no information available W provide an estimate of the num- ber of drums available for reconditioning nor an estimate of the precious mete] to be recycled. Other wastes potentially subject to a change of regulatory status include auto shred- der fluff, fluorescent light uibes/meroury vapor lamps, ethylene glyeoUantifreese and combustion ash. Estimates of these wastes will be added when their regulatory status is clear andlor methods for projecting the levels of these wastes are available. l 3.90 u TABLE M -PROJECTED QUANTlTiES OF NEW HAZARDOUS WASTE STREAMS Waste group Additional Pretreatment Other new wastes(1) Sludges (1) Waste oil Halogenated solvents Non-halgtd. solvents Organic liquids Oily sludges Non-halgtd. sludges Dye & paint sludges Meta]-containing liquids Contaminated soil Miscellaneous wastes (1) Data not availab]e as of January, 1988 u r1 L J Table M 3-91 r~ LJ Table N - - Tables N-1 and N-2 provide a summary and compilation of Tables K. L and M to ob- '' fain an estimate of the total hazardous waste projected to be generated in 2000. Two estimates are shown. The first (Table N•1), provides an estimate of the hazardous waste that would be genented if no additional eSort to minimize waste occurs. Table A'-2 provides a conservative estimate of potential waste minimization op- portunities using figures provided by DHS. R'hile it is believed further reductions can be achieved, an aeeunte assessment would require en inspection of each facility to assess current management praetias. The level of reduction achievable is depen- dent on the eurnnt waste management practices and the manufacturing processes used by local industry and this is cite specific. As indicated earlier, it is expected that clean ups from removal of underground storage tanks and asbestos in schools will be completed prior to 2000 and thus are not included in this projection. Figure N illustrates these data Figure N Projected Quantities of Hazardous Waste Shipped Offsite in 2000. Waste oil Bagnousc waste Oiiy sludges Linspeeified sludge ~ Non-halgtd.soivents - Metal rntg. liquids - Miseellanwus - Other inorg. waste Metal containing sludges ~ Non-mtl. inorg. liquids ^ 5000 10000 15000 Tons 20000 25000 30000 3.82 Table N • TABLE N•1 • TOTAL PROJECTED QUANTITIES OF HAZARDOUS WASTE SHIPPED OFFSITE IN 2000 (1) Assuming no waste mini mization Waste group Projected Projected Projected Projected Total Industrial clean up new Household waste (2) waste (3) wastes (4) wastes (5) Tons/year Tons/year Tons~year Tons~year Tons/year Waste oil 28,077.85 991.20 29,069.05 Halogenated solvents 271.69 271.69 Non-halgtd. solvents 4,669.99 4,669.99 Organic liquids 381.55 718.62 1,100.17 Pesticides 180.60 123.90 304.50 Oily sludges 7,228.71 7,228.71 Halgtd. org. sludges 363.51 363.51 Non-halgtd.org.sludgea 326.26 7,304.27 7,630.53 DyeE,paint sludges 486.04 486.04 Iv4etal containing liquids 3,857.68 42.00 61.95 3,961.63 b4eta]containing sludges 1,313.18 1,313.18 ?: on-mtl. inorg. liquids 936.98 61.95 1,000.93 Non•mtl. inorg. sludges 53.91 53.91 Contaminated soil 28,728.71 28,728.71 ~fiscellaneous 0.00 141 Off-spec. inorganic 38.49 38.49 162 Other spent catalyst 22.26 22.26 172 Metal dust 183.32 183.32 161 Other inorg. waste 1,533.43 . 2,809.33 30.96 4,373.74 322 Biological waste 1.62 1.62 331 Off•spee. organics 46.82 46.62 491 Unspecified sludge 6,142.50 6,142.50 511 Pesticide coat>30 g 87.46 87.46 512 Empty cont.>30g 476.60 476.60 513 Empty cont.<30g 481.06 481.06 541 Photo waste 337.65 337.65 551 Laboratory waste 40.25 40.25 561 Detergent b soap 54.55 54.55 591 Baghouse waste 9,249.76 9,249.76 612 Household waste 23.34 23.34 Total 66,869.46 38,884.31 1,988.60 107,742.37 (1) This Table includes data projections for wastes currently managed offsite. It is assumed the wastes now treated and/or disposed on-site will continue to be managed on-cite. Please see Table K for an estimate of the ]eve] of those wastes in 2000. (2) Taken from Table K (3) Taken from Table L, (does not include tank removal wastes or asbestos removals) (4) Taken from Table M (5) This data is based on the estimated household hazardous aste generation level in Table I, multiplied by a growth factor of23.9%. Based on an ~timated population of 1,536,600 in the year 2000, compared to a current population of 1,239,967 in 1988. Source of estimated population: SCAG, "Draft Baseline Projeetion,1986". Current population figures from the California Department of Finance. 3-93 Table N • TABLE N•2 -TOTAL PROJECTED QUANTITIES OF HAZARDOUS WASTE SHD?PED OFFSTTE IN 2000 (1) Assuming waste minimization • Waste group Projected Percent Projected Projected Total Industrial Reduction(3) Ind. waste Clean up dt waste (2) wlreduetion HHW (4) Tondyear Tonslyear Tonslyear Tons/year Waste oil 28,077.85 8% 25,631.62 991.20 26,822.62 Halogenated solvents 271.69 9% 247.24 247.24 Non-halgtd. solvents 4,669.99 1% 4,623.29 4,623.29 Organic liquids 381.55 4% 366.29 718.62 1,084.91 Pesticides 160.60 .2% 176.99 123.90 300.89 Oily sludges 7,228.71 4% 6,939.T~6 6,939.56 Halgtd. org. sludges 363.51 9% 330.79 330.79 Non•halgtd. org. sludges 326.26 1% 323.00 7,304.27 7,627.27 Dye ~ paint sludges 486.04 5% 461.74 461.74 ?Metal containing liquids 3,857.88 25% 2,893.41 103.95 2,997.36 1,4etal containing sludges 1,313.16 25% 984.89 984.89 Non•mtl. inorg. liquids 936.98 25% 704.24 61.95 766.19 Non-metallic sludges 53.91 25% 40.43 40.43 Contaminated soil 26,728.71 28,728.71 Afiscellaneous • 191 Off-spec. inorganic 38.49 2% 37.72 37.72 162 Other spent catalyst 22.26 2% 21.81 21.81 172 Metal dust 183.32 2% 179.65 179.65 181 Other inorg. waste 1,533.43 2% 1,502.76 2,640.31 4,343.07 322 Biological waste .1.62 2% 1.59 1.59 331 Off-spec. organics 46.82 2% 45.86 45.88 491 unspecified sludge 6,142.50 2% 6,029.65 6,019.65 511 Pesticide cont.>30 g 87.46 2% 85.71 85.71 512 Empty cont.>30g 476.80 2% 467.26 467.26 513 Empty eont.<30g 481.06 2% 471.44 471.44 541 Photo waste 337.65 2% 330.90 330.90 551 Laboratory waste 40.25 2% 39.45 39.45 561 Detergent 8 soap 54.55 2% 53.46 53.46 591 Baghouse waste 9,249.76 2% 9,064.76 9.064.76 612 Household waste 23.34 2% 22.87 22'87 Total 66,869.46 62,266.40 40,872.91 103,141.31 (1) This Table includes data for wastes currently managed offsite. It is assumed the wastes now treated and/or disposed onsite will continue to be managed onaite. Please see Table R for an estimate of the level of those wastes in 2000. (2) Taken from Table R (3) Estimates of potentie] waste minimization are taken from DHS "Guidelines". These estimates are conservative. Amore accurate assessment of waste minimization potential would require an inspection of each generating fact7ity to determine current management practices. (4) Taken from Table N•1, two columns are combined. 3-94 • • • 8.4.1b Table O Table O provides information on projected commercial hazardous waste treatment and disposal capacity in San Bernardino county in 2000. Because Chemwest In- dustries has Sled a notice of e]osure, the existing capacity at that facility is shown as lost eapadty. Although there are several applications for facilities anticipated, it is too early in the design stage and permit process to include additional capacity at this time. 3-95 TABLE O • PROJECTED CONIIVfERCW, ue~estnOUS WASTE TREATMENT AND DISPOSAL CAPACITY IIV SAN BERNARDINO COUNTY (?A00) Generalized Eusting Proposed Losa of Total pro- Treatment Method capacity (1) faeilitiet (2) eapaeity(3) jetted cap'y. Tons Tonc Tons Tons Aq.T4eatment-Org. Aq. Treatment - M/N Incineration Solvent Recovery Other Recycling Stabilization Residuals Disposal 4.5 86,000 88;000 (1) Data from Table C. (2) Current and anticipated applications att too early in the design stage and permit process for inclusion at this time. (3) Data from Table C. 4.5 Table O • • 3-96 • i • 3.4.16 Table P Tables P•1 and P•2 provide two needs assessments for commercial hazardous waste treatment capacity based on the data provided in Tables N•1 and N•2. The projected generation levels were converted to a capacity needs assessment by using the as- signed treatment methods identified for each waste getup in Table A Table P•1 as- sumes no additional waste minimization will occur. Table P-2 assumes a conserva- tive level of waste minimization. r1 LJ • 3.97 TABLE P-1• PROJECTED NEEDS ASSESSMENT FOR CONIIVIERCIAL us~sRnOUS WASTE TREATMENT CAPACITY Assuming no waste minimisation Generalized treatment Projected cap'y Projected Projected eap- method requirement (1) capacity aeity excess(+) or deficiency(-) Aq. Treatment-Organic 306.12 -306.12 Aq. Treatment-Meta1/Neut. 1,000.93 -1,000.93 Incineration 363.5] 4.5 -359.01 Solvent Recovery 12,572.2]" -12,572.21 Oil Recovery 36,297.7E -36,297.76 Other Recycling 40,381.74 -40,38L74 Stabilization 16,820.1( -16,820.10 Total 107,742.37 4.5 -107,737.87 (1) Data based on total estimated wastes in Table N-1 and assigned treatment methods for each waste group as identified in Table A Table P • • 3-96 I• i• TABLE P•2 • PROJECTED NEEDS ASSESSMENT FOR COMMERCIAL HA7.AF{DOUS WASTE TREATMENT CAPACITY Assuming waste minimization Generalized treatment Projected cap'y Projected Projected cap- method requirement (1) capacity aeity excess(+) or deficiency(-) Tons/year Tons~year Tonslyear Aq. Treatment-Organic 302.48 .302.48 Aq. Treatment-Meta1/Neut 766.19 •766.19 Incineration 330.79 d.5 -326.29 Solvent Recovery 12,497.60 -12,497.80 Oi] Recovery 33,762.38 -33,762.38 Other ReeycIing 39,312.41 -39,312.41 Stabilization 16,169.26 -16,16926 103,141.31 4.5 •103,136.81 (1) Data based on total estimated wastes in Table A'-2 and assigned treatment methods for each waste group as identified in Table A Table P 3-99 M ~ SA.17 Table Q • Tables Q-1 and Q-2 provide information about the projected annual quantity of haz- ardour waste residuals nmainine after treatment which will require disposal in 2000. These figures were calculated using the projected eenention levels and treat- mentmethods developed in earlier Tables combined with a ncidual ~enentSon factor provided by DIiS in the Technical Reference Manual of the Guidelines for the Preoe- • 5.100 • r~ U r 1 LJ TABLE Q1 -PROJECTED QUANTITY OF RESIDUALS GENERATION Assuming no waste minimization Generalized Treatment Projected cap'y. Residue Projected Method Requirement (1) Generation Residuals Tons/year Multiplier (2) Tons/year Aq. Treatment-Organic 306.12 1096 30.61 Aq. Treatment-Metal/Neuk 1,000.93 509E 500.47 Incineration 363.51 1096 36.35 Solvent Recovery 12,572.21 2050 2,514.44 Oi] Recovery 36,297.76 2096 7,259.55 Other Recycling 40,381.74 Stabilization 16,820.10 1209'0 20,184.12 Total 107,742.37 30,525.54 (1) Data taken from Table P-1. (2) Based on Table E-2 of DHS "Guidelines for the Preparation of Hazardous Waste Management Plans, Technical Reference Manual". Table Q 3 -101 TABLE Q-2 -PROJECTED QUANTITY OF RESIDUALS GENERATION Assuming waste minimization Generalized Treatment Projected cap y. Residue Projected Method Requirement (1) Generation Residuals Tons/year Multiplier (2) Tonslyear Aq. Treatment-Organic 302.48 1096 30.25 Aq. Treatment-Meta1/Neut 766.19 5096 383.10 Incineration 330.79 1040 33.06 Solvent Recovery 12,497.80 2040 2,499.56 Oil Recovery 33,762.38 2040 6,752.46 Other Recycling 39,312.41 StabOization 16,169.2E 12040 19,403.11 Total 103,141.37. 29,30L57 (1)Data taken from Table P-2 (2) Based on Table Fr2 of DHS "Guidelines for the Preparation of Hazardous Waste Management Plans, Technical Reference Manual". Table Q • • • 3-102 3S DISCUSSION AND ANALYSIS OF DATA The date presented provide considerable insight into hazardous waste management practices in San Bernardino County and provide the basis for development ofhazard- ous waste management policies in the remainder of this Plan. First, it is clear from a comparison of Table A (hazardous waste shipped offsite for treatment and/or dis- posal) with Table H (hazardous waste treated and/or disposed on-site) that 95% of the hazardous waste generated in the County is treated and disposed in the County. This is illustrated in the accompanying Figure. Figure H-2. Comparison of On-site Treatment/Disposal with Offsite Treatment/Disposal is San Bernardino County 522% J ~ Off-site Treatment/Disposa] ~ On-site Treatment/Disposal 61,61778 7ont 1,173,755.7 Tone It is expected that an increasing amount of the hazardous waste now shipped offcite for treatment and/or disposal will in the future be managed on-site. For example, one major generator of Metal-containing liquids has obtained regulatory approval for on-site retycling operations, thereby eliminating a significant waste stream. A1• though this trend is anticipated, the projections provided in Tables K - Q do not in- clude an estimate of the extent of change from offsite to on-site management. While Chapter 5 establishes a framework for siting specified hazardous waste fadiities, clearly the data establish a need for applying the siting criteria and ]and use review procedures for on-site treatment and/or disposal facilities as well. This issue is ad- dressed in Chapter 8 of this Plan. The comparison of Tables P-I and P-2, assessing future waste generation levels un- c~erscore the importance of waste minimization programs for future waste manage- ment planning. Even an extremely conservative estimate of waste minimization potential provides significant reductions in wastes requiring treatment and/or dis- posal. It appears that planning for future facility needs will require several years' data to determine if the suggested trends toward waste minimization and on-site • treatment will occur. Because of the rapid growth in the County, policies to promote waste minimization practices by new business are essential to ensure that thic growth doesn't overwhelm the waste minimization gains made by existing businesses. 3.103 94.78% • The projected levels of clean up wastes raise an important issue. Two major eategori• es of clean up wastes, underground tank removals and asbestos removal from schools, are expected to be large during the planning period, but do not appear in the estimate of wastes generated in 2000. In both instances, large volumes of waste will be generated over a ttlatively short period of time, after which waste generation levels are anticipated to drop sharply. Hazardous waste management practices are in a state of transition. Thus, on the one hand, there are some immediate short-term needs for waste management facilities. However, our long-term needs are very dif- ferent. There is a need to independently assess the short-term facility needs and the long-term needs. Additionally then is a need to develop a strategy for managing wastes during this transition period in a manner which avoids building excess tttat- ment capacity. Of these short-term needs, the tank removal wastes appear to be eurnntly managed within the existing system without a problem. Based on the rom- ments received, that does not appear to be the case for asbestos waste. Theft is a short-term need for additional disposal capacity for asbestos waste. Before preseni- ingthe long-term needs analysis, however, several data deficiencies should be noted. 3.5.1 Data Deficiencies The main areas in which there is a significant deficiency in the data provided are listed and discussed below, in order of priority. VS'aste Minimization Onoortunities. A careful assessment of potential waste mini- • mization opportunities in San Bernardino County requires an in-depth inspection of each major generator within the county in order to determine the current waste man- agement practices, the extent to which waste minimization techniques are already incorporated into production processes and the feasibility of incorporating additional waste minimization techniques at this facility. Conducting such an assessment at each major hazardous waste generator cite will require additional staff trained in K•aste minimization and auditing techniques. This program is discussed in Chapter 4 and is assigned the highest priority for implementation. Pretreatment Wastes. The impact of amendments to the federal Clean Water Aet on local businesses and how that will affect hazardous waste generation levels is not known or estimated in this Plan. Clearly, however, it is important that San Bernar- dino County Department of Environmental Health obtain information about specific businesses subject to pretreatment requirements including the types and numbers of such businesses; specific pretreatment requirements; types and amounts of hazard- ous wastes generated by the ptttreatment methods prescribed; and waste manage- ment alternatives available for these new wastes. Assistance to local sanitation de- partments and individual businesses in complying with these requirements should be provided. Clean uo Wastes at Contaminated Sites. Another area of data totally lacking in this Plan is an estimate of wastes which will be generated in the clean up of known con- taminated sites within the county. Since the connty is not the lead agency in devel- oping asite mitigation plan at any of these cites, it does not have any rontrol over the timing of development of these plant. Nevertheless, several poliriea for DENS • cooperation and participation in site mitigation efforts aft proposed in Chapter 12. Automated Hazardous Waste Trackine Svstem. Pttparation of thin Hazardous ~- Waste Management Plan was greatly enhanced by the wealth of information avail- 3-104 • able in DEHS files--including those from the hazardous waste generator program, the underground storage tank program, the household hazardous waste program and the hazardous materials disclosure program. However, the information presently maintained in each of the separate hard copy files would be substantially morn a~ces- sible and useful if it were automated. Development of an integrated and comprnhen- sive automated data management system has begun within DEHS and should be pursued. tcevis~ne and UpCatane the Countv Hazardous Waste Manaeement Plan. Given the degree of uncertainty regarding the date presented, the absence of some information and the rapidly changing management practices by hazardous waste generators, it is essential that the data, the operating prindples and the policies contained in the Plan be reviewed and updated on a regular periodic schedule. 3.6 NEEDS ASSESSMENT 3.6.1 Background Legislation authorizing the preparation of county hazardous waste management plans requires that the county plan include "a determination of the need for addi- tiona] hazardous waste facilities to properly manage the volumes of hazardous wastes currently produced or that are expected to be produced during the planning period". (California Health and Safety Code Section 25135.1 (d) (5) • In the Guidelines for the Preparation of Hazardous Waste Manaeement Plans. DHS requires: 'The CHWMP shall contain three TSDF needs analysis based on the follow, ing three scenarios concerning existing on-site facilities in the county and off- site facilities, inside and outside of the county, that currently manage haz- ardous wastes produced in the county: (1) Existing facilities meet rules and regulations; and (2) Existing facilities do not meet the rules and regulations, and choose not to modify, or are denied a permit and close; and (3) Existing facilities are modified to meet rules and rngulations on an un- known time schedule. Thus, assumptions as W probability of modification in- cluding time frames must be included. In each of these three scenarios, include a contingency factor for un- anticipated increases in waste volumes." (Section 3.5.4 Guidelines) While the DHS Guidelines provide a methodology for performing the needs analysic for the first two scenarios; no guidance is provided for the third scenario. The ques- tions raised in developing a needs analysis for the third scenario introduce new is- sues into the management of hazardous waste. At the present time hazardous waste • management facilities in California are ell privately-owned and privately-operated. An underlying premise of this Hazardous Waste Management Plan is that, except for household hazardous waste, hazardoua waste management will continue to be carried out by the private sector under strict rngulation by the government. This 3-105 Hazardous Waste Management Plan spells out performance standards for locating and operating hazardous waste facilities and the framework for review of appliea• lions for these facilities. The Plan does not propose either publiclyowned or publicly operated facilities. Thus performing the needs analysis required for the third scenario requires knowledge of corporate decisions not general)y available. In-lieu of providing specific time frames, a worst ease scenario is provided. Regional Aooroseh. The needs analysis which follows provides an assessment of haz- ardous waste management capacity requirements for San Bernardino county. At the time of passage of legislation authorizing the preparation of a hazardous waste man- agement plan, San Bernardino County had been a member of the Southern Califor- nia Hazardous Weste Management Authority (Authority). The Authority was formed in 1965 through a Joint Powers Agreement between seven Southern Califor- nia counties and several rities. At that time the member jurisdictions agreed to an Action Program designed to ensure the deve)opment of programs and the siting of facilities sufficient to safe)y manage hazardous wastes generated within Southern California San Bernardino County continues to be e member of the Authority and continues to support a regional approach to safe hazardous waste management. The Authority agreement is based on the concept of "fair share" which the Agreement defines as: "every city and county in the region will accept responsibility for the man• agement of hazardous wastes in an amount proportional to the hazardous wastes generated within the dty or rnunty". Through the process of developing a Regional Hazardous Waste Management Plan, the concept of "fair share" has been evolving. Both the Authority agreement and the most recent "fair sham" polity statement are presented in Appendix C. The Authority is continuing to refine the "fair share" prin- ciples. 3.6.2 Current Needs Scenario Oae (Best cane) AssumptionG (1) Existing facilities (inside and outside of county) meet rules and regulations. (2) Free-market trade is allowed (i.e. then are no restrictions to moving waste be• tween counties) or inter-county agreements exist. (3) Wastes now being treated by an acceptable treatment method are being managed properly and eapadty exists to continue to manage these wastes. (4) Wastes now being landfilled without prior treatment will require additional treat- ment capacity. Facility needs assecement" Treatment method 1986 tons Aqueous treatment • organic 1.89 Aqueous treatment - metals/neut. 144.11 Incineration 188.61 Solvent recovery Oil recovery Other recycling Stabilization 1,136.72 212.54 5,880.18 8,477.19 Total 16,041.24 3-106 1987 tons Ave. tons 1.89 L89 91.25 117.68 28.03 108.32 28.14 582.43 379.20 295.87 5,097.65 5,488.92 13,586.82 11,032.01 19,212.98 17,627.11 • • Scenario Two (Worst race) Assumptions: (i) Existing commercial facilities (inside and outside of county) do not meet the rules and regulations and choose not to modify, or are denied a permit and close. (2) All wastes now generated in the rnunty and shipped offsite will require new treat- ment capacity. (3) All wastes must be treated and/or disposed within county. The facility needs assessment of Table B would apply. Treatment method 1986 tons 1987 tons Ave. tons Aqueous treatment -organic 1.89 1.89 1.89 Aqueous treatment - metals<neut. 263.53 384.26 323.91 Incineration 308.44 132.33 220.39 Solventreeovery 4,195.89 3,998.28 4,097.09 Oil recovery 17,857.07 19,201.74 16,529.41 Other recycling 28,249.11 29,949.27 29,099.19 • Stabilization 8,639.83 16,051.00 12,345.42 Total 59,515.76 69,718.79 64,617.28 Scenario Three (Intermediate case) Assumptions: (1) Existing facilities are modified to meet rules and regulations on an unknown time schedule (2) Al] facilities require modification and all modifications are delayed more than one year. Needs There will be a need to assist generators in learning about and evaluating a host of alternatives: such as, out-of--state treatment; safe interim storage; waste exchange opportunities; recycling opportunities; and on-site treatment methods. 3.6.3 Conclusion The basic purpose of developing a County Hazardous Waste Management Plan is to analyze present generation levels and management practices, assess alternative scenarios, and propose policies and programs which will affect future generation levels and management practices. This is a dynamic process. To the extent that pro- posed programs are implemented and successful, the facility needs assessments pre- sented here and the projected generation levels in earlier Tables will be dramatically • changed. For that reason, a determination of need for a facility should be made at the time of a facility siting decision and should be based on data available at that time. 3-107 3.7 GOALS AND POLICIFS/ACTIONS 3.7.1 GOALS G-3.1 To establish a amprehencive and aaura4 data base to assist in program de velopment and to asseu facility capacity needs G-3-2 To ensure that the data base it maintained and updated regularly so that pro- gram planning is based on current information 3.7.2 PoIicies/Actionc P/A-3.1 Because current data collection and management practices do not allow easy compilation or interpretation, this jurisdiction shall develop a compre- hensive automated waste tracking system that integrates data from all hazardous materials and hazardous waste programs. The system shall be based on geographical, physical xnd land use characteristics. P/A-3-2 Because DHS in their comments on the Draft Hazardous Waste Management Plan requires that the County identify defiaencies and prioritize the manner in which the County will address these deficienaes, this juris- diction shall address the following defiaendes: 1. Perform a waste minimization assessment of all major hazard- ous waste produdng industries grid assist them in achieving maximum waste minimization ac specified in Chapter 4; . 2. Identify industries subject to pretreatment requirements and assist them in achieving compliance; 3. Include estimates of clean up wastes from Expenditure Plan sites as they become available. P/A-3-3 Because improved data would enable the County to develop stronger policy on hazardous waste management and because local concerns change, this jurisdiction shall update the data on an annual basis and revise the County Hazardous Waste Management Plan at ]east once every three years. The background information and data shall be made axessibie to other agencies and jurisdietione whenever possible. • :~ • 3.308 CHAPTER 4 • • 4.1 INTRODUCTION WASTE MINIMIZATION Waste minimization is an umbrella term that refers to source reduction and recycling. Waste minimization, as used by the Environmental Protection Agency (EPA), denotes the reduction, to the extent possible, oC hazardous waste that is generated or subsequently treated, stored, or disposed. It includes source reduction or recycling efforts that: 1) reduce the total volume or quantity of hazardous waste, or 2) reduce the toxicity of hazardous waste, or both. Of the two approaches to waste minimization, source reduction is the preferred method of reducing wastes. Source Reduction Source Reduction is defined as any process that reduces or eliminates the amount oC waste being generated; it usually includes processes within the manufac[uring or operating system oC a business. Source reduction measures include process and equipment changes, Droduct reformulations, chemical substitutions, and improved maintenance and housekeeping practices. These measures reduce the amount of hazardous waste by decreasing or eliminating the need for hazardous materials, unlike methods that reduce the amount oC waste after it has been generated, the so- called end of the pipeline approach. Source reduction is a preventive measure that can often be implemented at a minimal cost to the generator. RccycIing Recycling refers to the onsite or offsite after method is cost effective and reduces disposal costs. a waste tither process. This raw materials Source reduction and recycling are identified as preferred waste reduction options under the EPA's use of the term waste minimization. Treatment technologies should be considered only after acceptable waste minimization methods have been identified. This priority for waste reduction differs from the State Department of Health Services (DHS) preferred options; the DHS includes treatment as a preferred waste reduction method (see following discussion regarding regulatory requirements). The DHS promotes the use of onsite treatment measures as a way oC decreasing a county's overall need for offsite facilities. The EPA priority is used in this Plan because the County considers source reduction and recycling as the optimum methods for reducing wastes. 4.2 REGULATORY REQUIREMENTS In the Hazardous and Solid Waste Amendments (HSWA) of 1984, Congress declared it to be the national policy that "...whenever feasible, the use, reuse, or reclamation of it is generated by a particular because it decreases the need for 4-1 r1 LJ generation oC hazardous waste is to be reduced or eliminated as expeditiously as possible. Waste that is nevertheless generated should be . treated, stored, or disposed of so as to minimize the present and future threat to human health.' Generators are required by federal legislation to certify that a waste minimization program is in place. The operator must sign a certificate that states that the generator 'has a program in place to reduce the volume and toxicity of route generated to the degree determined to be economically practical and that the proposed method of treatment, storage, or disposal is that practical method currently available to the generator which minimius the present and future threat to human health and the environment' (RCRA, Section 3002(b)). California legislation enacted in 1986 (SB 1500, Chapter 1509, Statutes of 1986) expresses a similar policy regarding the primacy of waste minimization. This legislation prohibits lead disposal oC untreated hazardous wastes after May 8, 1990, and also establishes an order of priority Cor the development oC new hazardous waste programs. The Department oC Health Services and the State Water Resources Control Board are directed to "promote the following waste management practices in order of priority: 1. reduction oC hazardous waste generated, 2. recycling of hazardous waste, . 3. treatment of hazardous wastc, 4. land disposal of residuals Crom hazardous waste recycling and • treatment.' The commitment toward waste minimization is also expressed is the requirement Cor generators to include in their biennial reports to the EPA and California Department oC Health Services a description of the efforts undertaken to reduce the volume and tozieity of waste and any achievements. Only planning and reporting requirements are specified in the legislation. There are no specific waste minimization requirements Der se at Dither the state or federal level. No other requirements were specified because cach industry has unique waste minimization needs making a regulatory approach very difficult to develop and strong economic incentives already exist to encourage industry participation. Studio done by federal agencies (EPA and OTA) conclude that estabtishing mandatory programs would not provide an incentive for industry to develop waste minimization programs. Instead, governments should provide the necessary technical assistance, education, and information is order to assist industry in its efforts. 4.3 BARRIERS TO WASTE REDUCTION Studies point to several barriers to reducing waste by industry. These include technical, financial, institutional, and physical barriers. Lack of technical information has often been cited as the most critical issue in regard to the development of waste minimization programs. These • barriers are briefly described below: - Technical barriers impede a firm's ability to develop, evaluate, or 4-2 t implement waste reduction methods because oC lack of information, tack of in-house expertise to evaluate and implement waste reduction, and absence of readily available technology. Financial barriers prevent a firm from undertaking a waste reduction project because oC funding inadequacies. Institutional barriers can be either regulatory constraints or lack of awareness and commitment at the decision-making level in companies. • Physical barriers such as lack of space on the property of the waste generator to instal] a facility or process, can impede waste reduction. Local governments have the ability to facilitate waste reduction programs by providing assistance to generators so that these barriers may be overcome. Local governments can establish ordinances that specify requirements for waste reduction, identify the contents of waste reduction plans, and institute procedures to determine the potential Cor waste reduction. 4.4 INCENTIVES FOR WASTE MINIMIZATION Regulatory changes have prompted many generators to take a serious took a[ reducing the hazardous wastes they generate. The land ban which • prohibits the disposal oC untreated hazardous waste in landfills by 1990 has been an impetus to the consideration of alternatives to Land disposal. Escalating disposal costs and the concern with the potential of environmental contamination from improper disposal have also contributed. The long-term liability oC disposing wane has caused concern because the full cost is unknown and liability insurance is either unavailable or prohibitively expensive.. All oC these issues are incentives to reducing the amount of hazardous waste generated because producing less waste lowers .disposal costs, lowers transportation costs, and establishes better public relations with the affected community. 4.5 STATE WASTE REDUCTION PROGRAM The DHS administers the California Waste Reduction Program; a program designed to assist and encourage industry to implement waste reduction activities. The program consists of regulatory incentives, technical assistance, information/technology trahsfer and economic incentives. The regulatory element promotes policies and regulations that encourage industry to move away from land disposal. The technical assistance component provides assistance to business regarding waste reduction technologies. The program consists of waste stream specific studies, operation of the California Waste Exchange, waste reduction audits for small businesses, direct assistance by Department staff, and joint studies with industry associations. The information and technology transfer component makes industry aware of economic, technical, and environmental • advantages oC waste reduction. This effort is accomplished by the dissemination oC information via different media (i.e., fact sheets, seminars, newsletters/catalog, biennial report). Finally, the economic element 4-3 assists generators with overcoming specific barriers to waste reduction. The Hazardous Waste Grant Program is part oC this element. The DHS sponsors the Hazardous Waste Reduction Grant Program. The program was established by AB 685 (Chapter 1030, Statutes of 1985) which created a state grant program to support hazardous waste technology research and development. The bill appropriates 1 million dollars annually for the DHS to sponsor research development and demonstration projects. The program funds innovative projects involving hazardous wastc reduction, recycling, or treatment. Grano arc available to private individuals, companies, universities, governmental agencies, and private organizations. The DHS selects projects that offer the greatest opportunity to significantly reduce hazardous waste generation is California. Grants are available in four stages: 1) feasibility studies, 2) project design, 3) construction, and 4) evaluation. 4.6 COUNTY WASTE MINIMIZATION PROGRAM San Bernardino County DEHS has had an informal waste minimization program since 1983. The program has consisted of providing waste reduction and management information to generators through the County hazardous waste generator program, distribution of waste reduction information through a quarterly newsletter scot to all hazardous waste generators in the County, and eo-sponsorship of a one-day waste reduction workshop with the University of California Riverside Extension Program. Recycling of waste is strongly encouraged through the existing program. The DEHS provides assistance with recycling efforts by providing information from the California Waste Exchange (CWE) to generators in the area. The CWE provides a directory of companies that recycle acids, metal containing wastes, waste oils, solvents, and other wastes. Additionally the CWE publishes a quarterly newsletter promoting exchange of waste between users. The State DHS makes the CWE available to industry as a means of promoting use, reuse, and exchange oC industrial wastes. To further assist with industry efforts in waste minimization, the DEHS maintains a limited library on waste minimization methods and resources which is available to generators on request. These efforts have been successful in promoting an awareness oC the need for waste minimization in the County. The data (sec Chapter 3) reflect an increase in offsite recycling oC waste oil and solvents. Several different industries have benefited from the existing waste minimization program. The auto dismantling industry provides as example of a successful accomplishment for the County and this particular industry. The County DEHS worked extensively with the auto dismantling industry and their trade association in recycling the amount of waste oil generated. Several auto dismantling businesses in the County were unknowingly disposing of waste oil directly on the ground. The DEHS worked with the trade association in developing effective and environmentally sound methods oC collecting and recycling the waste oil. As a result of these efforts, in 1987 one auto dismantler recycled 25 tons of waste oil, in comparison with the yur 1986 when no waste oil had been recycled. • • 4-4 County waste minimization efforts extend beyond business generation of hazardous waste. The household hazardous waste program has an effective program for recycling waste collected through the permanent centers and the one-day events. The County recycles latex paint, recovers solvents from oil based paint, and sends the remaining wastes to a rotary-kiln cement plant to burn as as alternative fuel. Waste oil and car batteries are also recycled. Asa result, the County has reduced the amount of household hazardous wastes going to Class I landfills by about 75%. The substantial reduction of waste was achieved because of the type of waste collected (i.e., waste oil, paint) and because the San Bernardino County household collection center is permitted to commingle waste for recycling or treatment (State Treatment, Storage, or Disposal permit). Further efforts to recover usable materials through recycling are being explored. The waste minimization efforts of the County are funded by fees generated through the hazardous waste generator program. The DEHS has considered other funding sources such as monies from the Farr Bill described earlier. 4.7 GENERATOR SURVEY In 1987, DEHS conducted a survey oC its generators. The qualitative survey was conducted through the inclusion of a questionnaire in the quarterly newsletter distributed to all generators. The survey Corm • requested a voluntary response for information. (Results are shown in Table 4-1.) The purpose of the survey was to determine, qualitatively, the needs of the generators with .regard to waste minimization. The questions were designed to elicit responses regarding waste reduction efforts and the type of waste reduction information generators needed in order to implement waste minimization. The survey did not intend to evaluate waste reduction efforts on a quantitative basis. More than 200 responses were received out of a possible 1500. Since responses were voluntary, no scientific basis Cor the sample size can be made, thus, the sample responses may not be representative of all generators. The responses are insightful, however. OC those answering, 134 indicated they had begun some Corm of a waste reduction program. The most common methods of waste reduction included recycling (both onsite and offsite) and source reduction including process and equipment changes and material substitution. Some generators stated using both source reductions methods and recycling. No measure oC actual reduction in wastes was reported. Generators were reluctant to comment on the effectiveness or ineffectiveness of their waste reduction efforts. The majority specified that their waste reduction efforts had worked. Avery small number oC respondents (about 6) provided comments such as an inability to locate companies that would accept certain kinds oC waste for treatment or recycling, certain chemicals could not be recycled, and a comment was • received on the high cost of offsite recycling. It is very difficult to establish any pattern Crom this information. Likewise it is difficult to correlate the County's efforts in waste minimization with the application 4-5 TABLE 4-1 HAZARDOUS WASTE GENERATOR SURVEY RESULTS 1. Do you have a waste reduction program in place? (i.e., have you taken any measures to reduce your waste?) [f yes, what? 2. Have these waste reduction methods worked? IC no, why not? 3. Have you considered recycling as a waste reduction alternative? 4. Would you use any oC the following services to begin a waste reduction alternative? Educational information about what other companies are doing. Consultation services. Reduction in permit fees. Low interest loans Cor capital expenses. YES NO 138 65 l19 15 117 55 ~c in Favor 12! 61 78 50 • • 4-6 • of waste minimization by these industries. A large majority oC the respondents did, however, Cind that the materials put out by the DEHS were helpful to their implementation oC waste minimization programs. Therefore, the County's role in providing information to industry may have assisted industries in the development of waste minimization programs. A significant number of those generators that did not indicate the use of waste minimization strategies, implemented offsite recycling of their waste. Also interesting were the responses concerning the type of services desired in order to implement waste reduction. By far, most interest was shown in receiving educational information about what other companies are doing. Second to this was the desire fora reduction in permit fees. 4.8 EXPANSION OF THE COUNTY PROGRAM Although present efforts to encourage and promote waste minimization have been successful, an expanded program is necessary to provide more comprehensive assistance to all industries, to document quantitatively the value oC these waste minimization methods, to maintain personnel with expertise in waste minimization as a resource for industry, and to ensure that local industry is taking full advantage oC waste minimization opportunities. • A permanent program will be developed that includes education, technical assistance, economic incentives, and recognition elements. Two full-time staff positions will be allocated to the program. The program will consist of the development of informational materials, presentations before trade associations, and the conduct oC workshops. The program will be a cooperative work effort between County waste minimization staff and County generator inspectors. The waste minimization staff will work directly with businesses which request assistance in the development of waste reduction techniques specific to their 'businesses. The inspectors will receive training and assistance by the program staff and will refer businesses requesting more detailed or individualized assistance. Funding Cor the permanent program will be derived by fees from the hazardous waste generator program and Crom land use review fees Cor new businesses submitting waste minimization plans. 4.9 WASTE REDUCTION GOAL Ideally in establishing a program such as this, some measurable goal defining level of accomplishment should be established to determine the effectiveness of the program. Unfortunately, such a task is not easily defined in this case. The mere reduction in volume (such as through a dewatering process) may produce less waste but the waste will be far more hazardous due to its concentration. Conversely, a waste which has been stabilized may show an increased volume but a reduction in toxicity. There is no simple, measurable relationship at this time which takes into account both volume and toxicity in a meaningful way. Also since the • potential for reduction using currently available technology varies by 4.7 industry type and by waste stream, a simple level of reduction cannot be ~% projected for all industry. 4.10 GOALS AND POLICIES/ACTIONS In order to reduce the overall amount oC waste generated in San Bernardino County, an expanded waste minimization program should be established. The following goals and policies/actions set forth guideline Cor the recommended waste minimization program for the County. 4.10.1 Goals G-4-1 To minimize the generation of hazardous waste in San Bernardino County, to the extent possible. 4.10.2 Policies/Actions 'P/A-4-1 Because reducing the amount of waste generated in this County is an effective mechanism for reducing the potential impact of these wastes to the public health and safety and the environment, and because legislation encourages the reduction, to the extent feasible, oC hazardous waste, this jurisdiction shall encourage and promote practices that wilt, in order of priority: 1) reduce the use of hazardous materials and the • generation oC hazardous waste at their source; 2) recycle the remaining hazardous wastes Cor reuse; and 3) treat those wastes which cannot be reduced at the source or recycled. Only residuals from waste recycling and treatment shall be land disposed. P/A-4-2 Because industry often lacks the technical information or in- house expertise to develop waste minimization programs, and additional resources are necessary at the local level to assist industry in developing such programs, the County shall expand the waste minimization program to include education, technical assistance, economic incentives, and recognition elements. Educa[ional materials and technical assistance should be the first priority oC the program. Such information and assistance are the cornerstone to industry participation in waste minimization efforts. Other measures, like economic incentives and recognition measures, should also be implemented, but these are of a lower priority. The program shall consist of, but not be limited to, the following components: EDUCATIONAL ASSISTANCE: - Develop an expanded educational program on waste • minimization that includes: 1) brochures, Dublications, and 4-8 • posters to alert the public and industry on the importance oC waste minimization as well as describe appropriate reduction technologies and 2) audiovisual aids on waste minimization that can be taken to businesses, trade associations and public meetings. - Hold seminars and workshops for industry on waste minimization techniques and regulatory issues. Some of these seminars or workshops could be co-sponsored with local universities, Chambers oC Commerce, or the DHS. - Encourage trade associations and industry to Corm an industry task force to promote information exchange. - Maintain library oC technical reference materials and prepare a waste reduction resource directory. TECHNICAL ASSISTANCE - Hire a waste minimization specialist to coordinate the program implementation and provide on-going assistance to generators on waste minimization techniques. - Provide training to hazardous waste generator inspectors • on waste minimization techniques. The inspectors will incorporate waste minimization assessments into routine inspections and should be knowledgeable about the effectiveness of these techniques. - Provide waste audits on request and incorporate into routine inspections. ECONOMIC INCENTIVES - Provide information on availability of pooled loan fund and state grants Cor developing innovative technology - Reduce permit fees for firms that achieve waste minimization. RECOGNITION OF OUTSTANDING PROGRAMS - Develop a method for recognizing firms that have achieved notable success in reducing hazardous waste. Also, the program shall assist industry in preparing state and federal waste minimization reports. A copy of the report shall be submitted to the County DEHS at the time of permit renewal so that an annual report can be developed to measure the progress oC waste • minimization efforts. The annual waste minimization report prepared by DENS shall identify activities undertaken by the department and 4-9 >~ • provide some indication of the amount of hazardous wastes reduced as a result of Local efforu. P/A-4.3 Because having the County conduct a waste minimization audit is s voluntary action by a business and those businesses that participate may not be in Cull compliance with regulatory requirements, the County shall address violations as specified in state law. The. County shall develop in conjunction with the District Attorney policies Cor deciding on such violations pursuant to the requirements set forth in Section 25552 of the California Health and Safcty Code. The policies developed to address such violations shall include, but not be limited to, the following: 1) Whether the action is a knowing, willful, negligcnt, or inadvertent violation; 2) Whether the violator agrees to the schedule of compliance specified by the County; and 3) Whether the violation was discovered during an onsite consultation carried out pursuant to this chapter. In addition, the County may take enforcement action, or refer the violation for enforcement action, in accordance with state lew. • 4-10 • REFERENCES CHAPTER 4 -WASTE MINIMIZATION California Department of Health Services, Development Section, Alternative Technologv for Re~~~lin¢ and Treatment of Ha ardo« Waste. July 1986. 2. California Department oC Health Services, Alternative Technology Section, 1"iu idelines Cor the. Preparation of Hazardnu< waer~ wtana¢ement Plans. June 1987. 3. California Department oC Health Services, Alternative Technology Section, California Waste Exehan¢e - Directory of Industrial RewetGee 1988. 4. U.S. Environmental Protection Agency, Hazardous Waste Engineering Laboratory, The EPA Manual for Wastc Minimization Opportunity Assessments. EPA/600/2-88-025, April 1988 5. U.S. Eavironmental Protection Agency, Office of Solid Waste and Emergency Response, Waste minimization - Environmental Quality - with Economic Benefits. EPA/530-sw-87-026, Washington, DC, Octobet • 1987. • 4.11 i CHAPTERS SITING OF SPECIFIED HAZARDOUS WASTE FACILITIES 5.1. INTRODUCTION Responsible hazardous waste management involves not only encouraging waste minimization efforts but also providing a portion of the commercial facilities that will be necessary in the region. In order to ensure that facilities are located only in appropriate sites, procedures for evaluating a facility application and standards for review are necessary. These issues have been addressed in AB 2948 (Chapter 1504, Statutes of 1986) and the 'amending legislation SB 477 (Chapter 1167, Statutes of 1987),AB 3206 (Chapter ]389, Statutes of 1988), AB 3209 (Chapter 378, Statues of 1988), and AB 34 (pending). The act establishes procedures for consideration of hazardous waste facility applications and development of local criteria for siting facilities is the County. In addition, the net acknowledges the need for public input throughout the process and requires several avenues • for public participation. State law requires County Hazardous Waste Management Plans (CHWMP) to identify hazardous waste facilities that can be expanded to accommodate projected needs. The -aw also specifies that the CHWMP include siting criteria and the designation of general areas where the criteria might be applicable. Actions regarding land use approvals, planning requirements, or the siting criteria are included in the state law, as well :s time frames Cor the review of hazardous waste facility applications. More detailed information on state requirements is presented in Chapter 1 and APPendix B. The focus oC this chapter is to discuss the application review process. The chapter identifies local mechanisms that must be adopted into the General Plan and implementing ordinances to ensure that facilities are located in environmentally appropriate sites. The General Plan is a comprehensive long term document that identifies the County's goals, objectives, 'and policies for development is the unincorporated areas oC the County. Each oC the cities has its own general plan that applies to the incorporated areas within iu jurisdictions. The adoption or amendment oC the General Plan is a legislative net subject to initiative and referendum processes. The CHWMP is as element of the County General Plaa. Each oC the cities within the County has the option oC adopting the CHWMP or its equivalent. This plan recommends each City adopt the CHWMP as an element of the City General Plan. • 5-! 52 DESCRIPTION OF SPECIFIED HAZARDOUS WASTE FACILITIES Specified haurdous waste facilitiu are defined by the California Hulth and Safety Code as offsite facilities that accept wastes from more than one geacntor. By law a waste is defined as haurdous if it poses a threat to human health or the environment when not handled properly. A facility must have carefully engineered and designed means [or acceptance, storage, and treatment of the wutes as well as trained personnel operating the site. Specified haurdous waste facilitiu encompass a variety of different types and teehaologiu. It is important to dacuss the major types of facilities to provide a basis for the kinds of facilities that could be Droposed in the County. The discuuioa below presents the basic typo of specified haurdous waste facilities. 521 Transfer and Storage Facilities Transfer and storage facilities collect small quantities of haurdous waste and store them until it is economical to transfer the wutu to a treatment or disposal site. These facilities have often been associated with small quantity generators. There are two different types of transfer and storage facilities. The first type collects like wastes Crom many small generators (such as waste oil, solvenu, or dry cleaning materials). The wastes are brought to the facility in a facility-owned truck for temporary storage. The commingled wastes are later transferred to another facility for treatment. Operations of this nature are located in San Bernardino County and include Safety Kleen in Highland ss well as uveral waste oil • transporters The ueond type of transfer and storage facility generally accepts wastes of any type whether solid or liquid, brought is either by the generator (if it is a small quantity) or by a licensed tnnapotter, or by a facility-owned truck. While transfer and storage facilities are usually associated with small quantity generators, they can be used for large generators as well. Such CaciIities, although considerably larger, use a similar process Cor handling and storing wastes Presently, there are no such facilities serving large generators in the County although various waste management firms have diuussed developing a major waste transfer facility that would transport wastes to treatment or disposal facilities ouuide of San Bernardino County and out of state. Some of these large facilities may Dropou uu oC nil for long disunce transport. 5.22 Tratment Facilities According to a Depattl:tent of Hulth Services publication, 'Alternative Technology for Recycling and Trutmeat of Haurdous Waste', treatment facilities generally toe one oC the following Drocesses: 1) destruction or detoxification to transform a haurdous waste into a material safe for disposal; 2) concentration or volume reduction to facilitate the safe handling and disposal of haurdous components; and .. S-2 • 3) immobilization to isolate the hazardous components from the environment. Treatment facilities alter the chemical form, toxicity, or volume oC a waste. Because the treatment oC waste don not conserve materials, it is the last choice proeeu before dispoul in the hazardous waste management hierarchy. Treatment facilities leave a h:zardous waste residue which require disposal. These treatment facilities can be developed both onsite or offsite. Transportable Treatment iTnits (TTUs) ire temporary, mobile facilities that treat hazardous route at the site oC generation. They are becoming more popular because hazardous waste does not need to be transported long distances wad most versions oC treatment technologies are being developed as transportable units. In addition, most companies do not generate a sufficient amount of waste to warrant the expense of a permanent onsite facility and thus companies are beginning to recognize the advantage of TTU's Although TTUs offer an alternative to the development of large treatment facilities, local governments must ensure these facilities are operated in the most environmentally sound manner and that precautions are taken to ensure protection of environmental resources. Therefore, standards for the use, review, and approval of these facilities arc necessary. • Incineration is used for some wastes such as organic liquids and solids which cannot be reclaimed economically or are technically difficult to treat. Incinerators destroy the waste, leaving a small hazardous waste residue. They can be developed as onsite or offsite facilities and are often used is hospitals to burs infectious wastes. Like the TTUs, mobile incineration units are being proposed and may be more widely used in the future. Local governments must, however, ensure that facilities are placed in the most environmentally sound locations. The cement kiln incinerator has received favorable evaluations because hazardous waste can be used as a secondary fuel in the production of cement. Where coal or fuel oil is used as the primary Cuel, the use of hazardous waste is a secondary fuel may offer the potential to provide a net beneficial impact to air quality. Kilns have the capacity to destroy large amouau of wastes as well as recover substantial amounts of energy from certain solvents and waste oils One such incinerator is euttently operating in Lebec, California. It uses solvents from the painting, printing, and petrochemical industries u supplemental Cuel. A study done in New York State regarding the use oC cement kilns found that existing cement kilns could be modified at a relatively low cost to accept hazardous waste fuels. There are cement kilns operating is the County of San Bernardino which should be encouraged to use alternative aoureea oC energy, if a beneficial impact to air quality can be demonstrated. ~olidifieation and stabilization are the two most common methods oC immobilization. Solidification/stabiliution involves changing a liquid co a • solid or altering the characteristics of a solid to immobilize 'the contaminants. A variety oC materials are used including cement, lime, and S-3 ....~ .. polymeric materials. This method is used for wastes that cannot be • recycled, nested, or denoyed. Often, w:arcs undergo several treatment methods; solidifieatioa or stabilization is usually the last method applied in a treatment train. 523 Reey~r-~ FaciIitia Recycling involve the reclaiming, use, wad reuse oC wastes. A w:ate can be recycled onsite or offsite. For onsite facilitiu the waste is processed wad then reused or used for other pnrpoae. Offsite facilitiu would involve transporting the waste to a facility for procaring and then returning it to the generator or selling it oa the open market Recycling is a preferred waste processing method in the hazardous waste management hierarchy because it reduces the amount of hazardous waste ss well as conserve materials. 524 Residuals Repository and Land Disposal Methods Existing hazardous waste legislation refers to ruiduals repositoriu as a disposal method for future management oC waste. AB 2948 (Chapter 1504, Statutes of 1986) has as one of its goal that •ss an alternative to traditional land disposal methods, ruiduals repositoriu be utilized for the byprodueu of preferred hasrdous waste treatment tcchnologies.• A ruiduals repository is defined is sate law (SB 2093, Chapter ld17, Statute of 1988) as a specified hazardous wsste faeiIity which accepts only treated hazardous waste, meets all applicable federal wad state regulations, wad holds s hazardous waste facility permit A residuals repository would provide for the disposal of raidual material remaining from treatment of hazardous waste. While the defiaitioa of a residuals repository specifies that only trotted waste would be accepted. certain waste such ss contaminated soils may also be disposed of at a raiduals repository. Contaminated soils with hydrocarbons are temporarily exempt from the landfill ban oa disposal of untruted hazardous waste established by the Hazardous and Solid Waste Amendment of 1984. In addition, state taw require the State Department of Health Services (DHS) to develop standards Cor ruiduals repositories by May 1, 1990. la developing the suadards, the DHS must consult with applicable state and federal agencie and the public. The standards must include the types of waste acceptable for disposal at a ruiduak repository, standards for the design and construction of the facitiry, suadards for the operation, monitoring, mainteaantx, elosnre, and post-elosnre of residuals repositories, standards for the location oC the facility and subsurface geology, and requirements for hazardous wasu segregation and reeordkeepiag.. Siaee disposal faeiIities, other than repositories, may be proposed in the County, thue othcr types oC facilitiu must also be included is the discussion of airing specified hazardons waste faeitities. Identifying only the ruiduals repository method eliminates facilities like landfills, deep- well injection, wad land sprading. To addreu this group oC facilities, the state defiaitioa of lead disposal method is also used. The California - Code of Regulations (CCR), Title 22, define lead disposal method as the 5-1 disposal, storage, or treatment of hazardous wastes on or into the land, including, but not limited to, landfill, surface impoundment, waste piles, deep-well injection, land spreading, and co-burisl with municipal garbage. The definition of a land disposal method encompasses several different technologies for managing wastes. The term lead disposal method is used in this plan along with the residuals repository concept because together they address the different types of land disposal options. When the term land disposal facilities, is used, it rcfers to land disposal method and residual repository collectively. ' 525 Discassioa The land arca requiremcnts for the different specified hazardous waste facilities vary significantly based on the size and type of the proposed facility. For instancc, a land disposal facility would require large amounts of land and, thus, would be more appropriate to site in remote or less populated areas. The State DHS has estimated the land arca requiremenu for different facilities. While the actual sizes and necessary land areas vary significantly, the estimates provide a good basis for comparing the difCcreat facilities. The physical eharacteristiu of the facilities :re presented is Table 5-1. Whereas a land disposal facility (using estimates for the residuals • repository) may require anywhere from 50 to 300 acres of land, a treatment facility could require anywhere Crom 3 to 30 acres of land. It is evident from these estimates that a land disposal facility could be sited in rural or dcsert lands because of the need for larger land areas, if applieablc environmental concerns were addressed. Siting of specified hazardous waste facilities in any area must include consideration oC buffer zones. The amount oC truck traffic would be as important consideration in siting a facility. For example, a small treatment facility could generatc !2 to 14 trucks per week whereas a large facility could generate a significantly higher amount of truck traffic, around 120 to 300 truck. trips per week. Thus, proposed transportation routes must accommodate anticipated truck traffic. la addition, aesthetic issues must be addressed since most of thesc facilities could have visual impacts as well as air quality concerns since facilities have the potential to generate air emissions. • 5-5 - .. ~. ~ . C V t ..~ r ~ N ~ D r ~ ~ y a e ~ O y O y O C 7 q o C7 b y n L O q j L D-~+ p 0 [ q9 N Y Y L S O ~ O O P7 Ofr OLC LY CL M Y 0 Y 4 qr 1 i 7 Cll.i SiL N^ n O ? 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I n M M O A H .I 1 1 N n n e 1'1 V N ~ e n ~ N ~1 e O P M 1 • 1 O a ~ ' .I O i .~ p I q Y ~ N > L r O LI , p ~ 6 9 U V O N V c e °> 7 e O o ~l u 7 .r y UL q 1 N eyy Y O e47 t ..l y O III rv - n N O N ry O O O O n nl 1 O O N n n O 11 1 O L1 M f a O l1 Y .I 1 y ~ 1 u ~ m a n L L y .r !~ !1 7 7 O O al •I ! a ~ J '' 'D 7 . S ~ a a ~ ~ O O ee x.r z.. .. J J O O 'r O q oa nO Y J a Y M V 3 3 1 I O O r+ .1 q O a+ a•I ee ^ L O :~ y 7 ~ M Y L • C C ° n ~ c I i o m > > n ` r a ... O q q « O ~ + . E o p ~ p o q F NN M V .~M C 0 Y O L L O J J 0 D. V N a O O G 7 r H O 7 a r 7 q 1.! ^•I Dy v u ~ E D P O O L7 n ~` ti O OY o a O O ++ 'o C7 O. ^ e .+ w L q q O V ao N V 5 O H n vl 53. LOCAL SITING PROCESS TO COMPLY WITH THE,TANNER ACT • Development of specified haurdous w:ste facilities requires pcrmits from state and local agencies. The State Department of Health Services is responsible for issuing 6aurdous waste facility permiu and Cor ensuring that operating conditions impoud on the approval of a facility are met It is the responsibiiity of local governments, however, to sec that a facility is aired is areas with compatible land uses, to ensure that eonditions'of approval on land uu permits arc implemented sad carried out for the duration of the project and to respond to hazardous material/waste emergencies At the local level, both discretionary sad ministerial land ttu permits would be required. Local land use authority is derived From police powers which were reserved to the statu by the Federal Constitution and delegated to cities sad counties in California by Article XI, Section 7 oC the State Constitution. The local review procedures would be similar to the consideration given other major industrial facilities with the addition of the review and public participation requiremenu identified in AB 2948(Chapter 1504, Statutes of 1986), et al. These additional review procedures were added by state law to ensure that proposals for specified hazardous waste facilities were adequately evaluated and public participation occurred throughout the process The following discussion looks at the three major issues involved is the local siting of specified haurdous waste facilities: a) the need for . specific land tree daigaatioas addressing specified hazardous waste facilities, b) the development of local siting criteria, sad c) the local application review process ,.-% 53.1 Lead Use Designation for Hazardous Waste Facilities Significant public concern was ezpresud regarding the siting of a facility in areas where future incompatible uses could be permitted. To address this concern, project prot>osaks may only be sited with a site approval (Conditional Use Permitt) is areas zoned with a specified h:zardous waste facility overlay which applies to the project site and corresponding buffer. An overtay zone applies an additional level of regulation since the applicant meter comply with both the base dtstrict (zone) and overt:y zone requircmeats The overlay zone, however, provides more dctail than the bau zone oa the appiicable land uu review requirements, compatible land uses, and say special permit procedures which are unique to specified hazardous waste facilities. The nu oC the overlay ensures that any future proposed land uses within the overlay are compatible with the hazardous waste facility. The overlay is not assigned to any particular location on the zoning rasps until approval for a specified hazardous waste facility has been grated, hence the term floating overlay. Although the overlay zone is not given a specific location, the overlay must be 1 The County of San Bernardino refers to its dtscretionary land use aDPlieation u a 'Site Approval'. It is equivalent to a conditional uu permit application. • s-a - • described in the County Development Code (zoning ordinance) as a requirement The County must amend the Development Code (zoning ordinance) in order to require and define the overlay. The zoning ordinance amendment is necessary because current land use documenu do not address permitting requirements or procedures Cor specified hazardous waste facilities (see Policy P/A-5-4). The County Development Code must identify the purpose and need for the zoning overlay, when the ovcrley is applied, and any special requirements (siting criteria and General Plan policies) that must be met. The Development Code must also identify specific land use distrieu (or zoning) where the overlay may be applied. Land disposal facilities may be sited in areas not projected to receive pressure for eztensivc development since these facilities hold wastes for long periods of time and require larger land areas found in the Resource Conservation district The Resource Conservation District applies to "eztensivc areas of public and private open space which by their location, access limitation, natural resources or scenic qualities are suited for little or no human habitation' (County Development Code, Section 85.0405). This District (zone) allows for a wide range of uses ranging from residential and manufacturing to resource production and extraction likr mining activities. A major part of the areas zoned for Resource Conservation are the desert lands which comprise about 9596 oC the lands in the • County. A significant portion of the desert areas, however, are federal lands which are not under the jurisdiction of the County. Treatment, recycling, storage, and transfer facilities should be sited is the Regional Industrial District (heavy industrial or equivalent). The Regional Industrial District 'creates, preserves and enhances areas for heavy industrial uses which cause moderate to high degrees of environmental nuisances or hazards' (County Development Code, Section 85.0475). 53.2 Siting Criterit State law requires the CHWMP to include siting criteria and designate general areas where the criteria might apply. Siting criteria set forth a structure for evaluating Droposals for specified hazardous waste facilities and serve to focus the evaluation of facility proposals on critical issues. Siting criteria represent a uniform set of standards applied to all applications, yet they are designed with some Clezibiiity depending on the type of facility and the proposed site location. Siting criteria are used for evaluating a project at a particular site. When used along with general plan policies, the siting criteria de[ermiae the suitability. of a site for a specified hazardous wazte facility proposal. The use of the siting criteria sad General Plaa policies are part of the full application review and environmental saalyzis required of all applications Cor specified hazardous waste facilities under state law. The 'Guidelines for Preparation of Haurdous Waste Management Plans', • prepared by the State DHS, include a set of siting criteria that may be adopted by the County. These criteria are based in part on criteria 5-9 '~ i developed by the Southern California Hazardous Waste Management Authority. The criteria presented herein were developed from the State DHS criteria and input Crom the CHWMP Advisory Committee, public comments received at workshops and hearings, and written eommenu from cities and other responsible agencies. The criteria meet the local conditions and concerns of San Bernardino County u well as provide Cor the protection of local environmental resources and public health and safety. A summary oC the criteria are presented in Table 5-2; the complete criteria are included at the cad of this chapter (atarting.oa page 5-2d). The siting criteria are development standards applicable to the development of all specified hazardous wssu facilities. Aa applicant. for a specified hazardous waste facility must demonstrate consistency with the siting criteria and the policies of this plan in order to receive approval of a specified hazardous waste facility application. _ The siting criteria may also apply to Transportable Treatment Uniu (TTUs) since they have the potential to impact the environment The Guidelines prepared by DHS define TTUs as 'hazardous w:ate treatment works which arc designed to be moved either intact or in modules and which are intended co be operated at a given location for a limited period of time.' Further, the Guidelines state that TTUs are considered onsite facilities if they are treating wastes at the site of generation, or, if TTUs are used for site mitigation or emergency rapoau purposes When TTUs are need for trating wastes that havc been removed from a generation site, such u transfer stations, the sate considers TTVs to be consistent with .existing permits While they are temporary facilities, TTU'a haadlc wastes similar to stationary fuiiities and, thus, could have a sigaificaat impact on the environment Many hazardous waste generators in the County arc located is or Dear residential areas Locating TTUs is these areas would be inappropriate because of the facility's proximity to residential or tight commercial uses. These legal non-conforming land uses have resulted from rapid growth in the County. To ensure protection of public health and safety the siting criteria may apply to TTUs proposed is these areas Therefore the applicability of the siting criteria to TTUs will be determined on a case• by-case basis State law also requira connties to designate general areas where the siting criteria might apply. Not all the criteria could be mapped on a eounry-wide basis The list of maps used to evaluate the siting criteria is presented is Table 5-3. The maps (see Appendix F) illustrate that after aDPlyiag the available siting information, the criteria do not unreasonably eliminate all lands in the County for development of specified hazardous waste facilities The maps, however, are only a demonstration of the criteria's reaaoaableness and should only be aced as general guider Evaluation of an application for a specified hazardous waste facility should be baud on the siting criteria, adopted General P-an Maps which indicate appropriate areas for similar industrial development, a thorough environmental analysis, General Plan policies, sad the provisions of local ordinances. 5-10 • • • TABLE S_2 SUMMARY OF THE RECOMMENDED STITNG CRITERIA `J PROTECT THE RESIDENTS OF SAN BERNARDINO COUNTY 1. Proximity to Residences 2. Proximity to Immobile Populations 3. Proximity to Pub[ie Facilities 4. Provision of Public Services ENSURE THE STRUCTURAL STABILITY OF THE FACILITY 5. Flood Plain Areas 6. Proximity to Active or Recently Active Faulu 7. Unstable Soils PROTECT GROUNDWATER QUALITY 8. Dep[h to Groundwater 9. Major Recharge Areas for Aquifers 10. Pcrmeability of Surficial Materials • PROTECT AIR QUALITY 11. Noa-attainment Air Areas 12. Criteria Polluunts in PSD Areas PROTECT ENVIRONMENTALLY SENSITIVE AREAS 13. Wetlands 14. Habitat of Thrcateaed, Rare, or Endangered SDceies 15. Prime Agricultural Lands 16. Recreational, Cultural, and Aesthetic Resources 17. Areas of Potential Mineral Deposits LAND USE RESTRICTION 18. Military Lands ENSURE SAFE TRANSPORTATION OF HAZARDOUS WASTE 19. Prozimiry to Areas of Waste Generation 20. Prozimiry to Major TranSpOrtatlon Routes 21. Minimize Transport Through Minor Routes 22. Locational Restrictions Due to Transportation Routes • 5-I1 • TABLE 5-3 MAPS USED FOR EVALUATING STITNG CRITERIA' Alquist • Priolo Special Studies Zone Water Basin Exclusion Areas Endangered Species Habitat East Mohavc National Scenic Area Areas of Critical Environmental Concern Wilderness Study Area Military B:acs National Forest Areas Desert Tottoise Habitat Transportation Routes • Appeadiz F provides more detail oa these maps. • 5.12 ' • 533 The Local Application Review Process State law identifies a formal administrative process for the local review of facility applications The process provides for notification of affected agencies and the public of a pending application, procedures for the initial review and consideration oC as application, participation by the interested public through the local assessment committee, and a procedure for consideration of appeals oa a local decision made on a particular facility application. The procednres ensure a coordinated evaluation oC applications and inform the public and applicant of the requiremenu that must be met. In addition, the procedures specify and encourage public participation throughout the process. Refer to Table 5-4 for as outline of the procedures added to the local application review process by the Tanner Act The Office oC Permit Assistance (OPA) acu as an information resource on the application review process as well as a mediator to expedite the process and ensure that it runs smoothly. OPA has the following responsi bill ties: - assist in identifying state and local permi¢, - convene meetings concerning permit review, - assist state and local agencies in consolidating public meetings, - encourage the joint review and processing of applications, • work with aDPlieant and public agencies to ensure decision-making deadlines arc met, and call meetings or conferences to resolve questions or disputes State law also addresses the need to expedite review of applications for specified h:zardous waste facilities since several state agencies will also issue permits. to addition to local permiu, permits will also be required from the State Department of Health Services, the Air Quality Control Agencies, and the Regional Water Quality Control Board. In order to expedite the review process, a coordinated approach to the evaluation of applications is accessary. Three specific issues are identified in state law to assist is expediting the application review process. They are listed below: I) The applicant may submit two or more permit applications to public agencies for simultaneous review and processing, 2) Any public agency may request another public agency to jointly review applications, and 3) The Department of Health Services or any other state agency will • provide technical assistance to a local agency when reviewing an application for a specified haurdous waste facility. • 5-13 TABLE 5-4 SUI~fARY OF PERId1T PROCEDURES ADDED BY AB 2941 • Delegates specific duties and responsibilities to the Office of Permit Assistance (OPA), local jurisdictions, wad permitting agencies • Requires the project applicant to Cile a Notice of Intent with OPA wad the local land use jurisdiction before filing for a land use permit • Requires a seven member Local Assessment Committee to assist in negotiating the terms and conditions of project approval. • Requires the OPA to convene a meeting to inform the public on the proposed project and the application review procedures that will be followed. • Authorizes an applicant paid Cee Cor hiring an independent consultant to the Local Assessment Committee for revicw of the_projeet • Requires a meeting npfroat among lead and responsible agencies, project applicant, the Local Assessment Committee, and the interested • public to diseuu issues of public concern wad explain the application review process. • Provides for a written determination of a project's consistency with applicable general plans, development codes, wad the CHwlv>p. • Sets time frames Cor review and action by permitting :gentles. • Authorizes the establishment of a State Appeal Board and specifies the Board's composition, responsibilities, and appeal procedures • 5-14 • The procedures established in state law provide Cor a significant amount of public participation throughout the local application review process. Prior to adoption of these procedures, there were two formal avenue for comment on a local land use application: 1) Environmental Review process wader CEQA, and 2) project review and consideration. State taw has added several other avenues for public participation through the establishment of a Local Assessment Committee. The Committee works with the applicant and government agencies in evaluating the proposed projcet All meetings oC the Committee are public, therefore the public may provide input throughout the application review process. The requircmeau include a meeting prior to submittal of a formal application and again after the application is submitted to discuss public concerns regarding the project Outline of the Local Aoolieation Review Process- The types of applications required Cor local evaluation oC a specified hazardous waste facility proposal include both discretionary and ministerial permits. The information listed below only refers [o local land use requirements. The required Ioca1 land use permiu include: Appiicatioa to Apply the Zoning Overlay of 'Specified Hazardous R`ute Facility' to the project site and respective buffer (sec discussion in Section 5.3.1) • - Site approval application (Conditional Use Permit=) Special Uu Permit (iuued by the County Environmental Health Services Director, required as a condition of approval on the discretionary permit) Ministerial permiu from Building, Grading, Flood Control, etc. A Site Approval (Conditional Use Permit), or applicable city application, is necessary to site specified hazardous waste facilities in Saa Bernardino County. Along with the Conditional Use Permit application, an application to apply the specified hazardous waste facility zoning overlay is required for all proposed specified hazardous waste facilities. The overlay applies to the projcet site and associated buffer. Requiring the overlay res[rieu future development to uses that are compatible with specified hazardous waste facilities. The County of San Bernardino Land Management Department, Office oC Planning, or applicable City department would process the land use application. Other departments, such as the Environmental Health Services Department, will have a significant role in reviewing and commenting on an application. 2 The County of San Bernardino refers to iu discretionary Iaad uu application u a 'Site Approval". It is equivalent to a Conditional • Use Permit Application. 5-15 A Special Use Permit (SUP) should be included in the permit approval • process for development in a city or the County. The County Development Code (or Zoning Ordinance) specific that any use subject to an approved discretionary lead use app[ication •_ may also be made subject to the issuance of a Special U:c Permit• The County Environmental Health Services Department issues the SUP. The SUP ensures that development is monitored sad operated according to the conditions oC approval oa a -aad use decision. The SUP may be issued for limited time periods providing for periodic evaluation of a facility's adhereatx to project conditions. Specified haurdons waste facilities are complex projects which require as on-going sssasment of facility operations. The bat way to approach these periodic iaspeetioaa is through the requirement of the SUP. Couaty and city ordinance should be amended to identify specified hazardous waste facilitie as one of the uses requiring a SUP, the purpose aad intent of the permit, aad any special requirements that must be met For facilities tkat handle both hazardous waste sad solid waste, a solid waste Facility permit will also be necessary. The County Department of Environmental Health Services (DEHS) is the solid waste enforcement agency for both the title sad the County. The following information outline the local aDP[ieation review proeas for evaluating a specified hazardous waste facility proposal. The requirements added by sate law are included in the information below. Refer to Figure S-1 for an illusmtion of the items mentioned. The Figure iaelude a description oC the state proear Cor informational purpose since it may be a eoncmm~t process. a) At least 90 days prior to the submittal of a formal application the appiieaat must submit a Notice of latent (NOI) to the Office of Permit Assistance (ia the State Office of Ptaaniag and Research) and with the applicable city or County jurisdiction. The NOI provide a complete description oC the nature aad scope of the project The local agency aotifie the public about the proposed project by publishing notice is a newspaper oC general circulation, posting notice is the location where the project is proposed, and mailing notices to owners of property contiguous with the proposed project site. b) Subsequent to the NOI the Office of Permit Assistance convene a public meeting in the affected city or County to inform the public on the nature and scope of the proposed project The meeting also considers the proxdure aeeeary for review of a specified hazardous waste facility application. e) Within 90 days after reeeiviag the NOI the local agency appoiaa a seven member Local Assessment Committee. The Committee meets with the applicant to determine the terms and conditions Cor project approval. The aegotiatioas must focus oa the protection oC the public health aad safety aad the environment, as welt u the fistxl welfare through special benefits and eompeasatioa. The composition of the Committee eoasists of three representatives of the community - at large, two repraeatativa of environmental or public interest 5-16 - ' • groups, wad two representatives oC affected businesses and industries d) The applicant participates in a pre-application meeting which is set up with the local government agency (as required by the Health wad Satety Code, Section 25199.7 (e)). This conference provides as opportunity for the County and any applicable department to advise the applicant on project consistency with the General Plan and CHWMP before a formal application is submitted as well as to respond to questions regarding the permit process. Most cities have a similar procedure. e) Formal applications may be submitted to a city or the County once these initial steps have been uadertakea. Both the Site Approval Application (Conditional Use Permit Application) and the specified hazardous waste facility zoning overlay application are required. State law requires the permitting agency to decide on the completeness oC the application and [o notify the applicant regarding completeness within 30 days from the date the applications were su bmi tied. f) Within 10 days from the date the application was deemed complete, and within 60 days from the notice oC application completeness, the Office of Permit Assistance holds apost-application meeting among _ the lead and responsible agencies, the applicant, the Local Asseument Committee, wad the public. The purpose oC the meeting is to • determine the iuuu oC concern to the public and the permitting agencies. Oaee these issues have been heard the aDPlieant and the Local Asseument Committee meet regarding the terms and conditions acceptable to the community. The Act includes a provision Cor the Local Asseument Committee (LAC) to hire a consultant to review the project The apDiitsnt would pay a tee established by the local agency. In addition, iC diCferencu between the LAC and the applicant cannot be resolved, the OPA may recommend the use of a mediator. The applicant would pay half the cost for mediation. g) Whea the application has been found complete Dy the permitting agency, an initial study oC the project will be made to identify the significant impacts on the environment IC one or more significant impacts are identified then an Environmental Impact Report (EIR) is prepared. If no significant impacts are found or iC the significan[ impacts can be mitigated, a Negative Declaration will be prepared. When preparing an EIR the lead agency is required to send out a notice to all applicable agencies regarding the preparation oC the EIR. A scoping hearing can be performed by the lead agency to obtain public input After a Draft EIR has been released the public and responsible agencies have 45 days in which to comment on the adequacy of the Draft The Draft is considered by the Environmental • 5-17 F U 3 ~..~ Z U r_ U C ~:n H C h ~_ N U c.. h ~..i I ~.~ ~.. eQi y eao o L C Y ~_ y E 0 s ~ ~ = s d ~ C 'C ` ` ~ u ~ 'C ~~~ v ~' = 3 b +" u ~'-~ .i ~ G "a Y M M N u c ~R1 O i%9 r 6 0 e a, L .~ ~_ s 7 ~ n ~ ~ ~ E O k _ K N .S Q 4 O a ~ D ~ ~ v 2 h w ~ p .. C h ~ ~ ~axo ~ ~ ~ .+ u ' v u d ~ e y ~^ py D Z N ' i = r $ ~+ 1 n Y ~ a w E ~ ~ °S '~ » u S L I Z SS3JOad 31V1S • m ...i Il'ii ~~ ssaJOaa ~vJO't i ~. • Review Committee is a public meeting. The environmental document is certified by the decision-making body (in [his use the Board oC Supervisors) when a decision is made on a project. Refer to P/A-S- 4 for the issues that will be evaluated as pan of the environmental analysis. h) A noticed public baring is thew sehedulcd before the Planning Commission for consideration of the site approval (Conditional Use Permit) and appliution of the zoning overlay. A staff report is prepared by the lead agency which describes the project, any issues of concern, sad a recommendation for approval or denial of the land use applications. The Local Assessment Committee also prepares a report that is submitted to both the Planning Commission and the Board oC Supervisors or the City Council. It includes the Committee's recommendations for approval or denial of the project and any terms and conditions which have been negotiated. The Planning Commission forwards iu recommendations to the Board of Supervisors or City Council. A decision on the application is made by the Board of Supervisors or City Council, at a noticed public haring. Any interested person or the applicant may file an appal on the approval oC the project or the conditions of approval with the State Appcal Board, within 30 days of that decision. A decision on the appal will be based on consistency with an adopted, approved CHWMP. • i) A Special Use Permit is issued as a condition of approval on the Sitt Approval (Conditional Use Permit). The purpose of this permit is to ensure that conditions oC approval are carried out j) If no appeals are filed on the land use applications, ministerial permiu may be issued. These permits msy include permiu from building wad safcty, grading, environmental halth, flood control, etc. The set also authorizes the establishment of ea State Appeal Board and establishes appeal procedures. The most significant aspect of the responsibilities of the State Appeal Board is the requirement that decisions must be based on consistency with the CHWMP. The Govcrnor or designee may cstabiish the State Appal Board within 30 days Crom the date the appeal is received. The Aet states that the Board mus[ not reverse the decision of the local agency unless it can makc the following findings: - significant environmental impacts will be adequately mitigated, - the project was consistent with the General Plan when the local agency accepted the application as compicte, - the project is consistent with the CHWIvIP, - alternatives Cor the project (identified is the EIR) have been appropriately eonsidcred by the State Appcal Board, and - reversing the decision is consistent with statewide, regional, wad • county hazardous waste management goals, policies, wad objeetives- 5-19 A project applicant or nay interested person can Cile an appeal oC a local • decision or on a condition(s) oC approval to the Governor or designee. The appeal must be filed within 30 days of the local decision. A project aDpiitxnt may file an appal on the approval of t permit, but must specify the conditions in dispute and must prove that the land use decision was so restrictive that the approval wu equivalent to a disapproval oC the permit. Aay interested penoa may file an appeal on the approval of a permit. Such an appeal must demonatnte that the project does not adequately protect the putilie hulth, safety, or welfare. Aa appeal on the disapproval of a permit will only be accepted if all sate peratits, which can be issued before construction, are obtained or if a decision was made before environmental review was completed. State law requires the State Appeal Board to conduct meetings in the affected jurisdiction to solicit public iapnt 5.4 GOALS AND POLICIES/ACT10N5 The following goals, polieia, and actions shall be implemented to ensure that specified haurdous waste facilities are reviewed according to the procedures identified is sate Iaw and sited in the most environmentally preferred locations Tao terms are used to identify the implemeatiag agency. The term 'this jurisdiction' refer to the aDPlieable city or county. Where County and 'this jurisdiction' are used, the policy applies to both the County of San Bernardino and the applicable governmental body. 5.4.1 Goals G-5-1 To establish as effective and expeditious application revicw process for _siting specified haurdous waste facilities that includes ezteasive public participation. G-5-2 To apply a uniform set of criteria to the siting of specified haurdous waste facilities in the County for the protection oC the public hult6 and safety and the environment. G-5-3 To easun coordination among agencies and County departments is the review of all specified haurdous waste facility applications within the County. G-5-4 To protect vital groundwater resources Cor present and future bencfieial uses 5.4.2 Polieia and Actions Policies/Actions this )nrisdictioa Reonires of the Anolieant P/A-5-1 Because specified haurdous waste facilities shall only be sited in areas where land uses have been deemed compatible with • such facilities by the local jurisdiction, as applicant for a 5-20 ~ i • specified hazardous waste facility must apply for a Site Approval ( Conditional Use Permit) and a zoning amendment. The zoning amendment applies the SDeeiCied Hazardous Waste Facility overlay (as defined in P/A-5-4) to the project site and buffer area. The applicant shall meet sll provisions oC the specified hazardous waste facility overlay district (see Policy P/A-5-4) as well as other general plan and ordinance provisions P/A-S-2 Because the evaluation of a project application is a costly and time consuming effort and the public involvement demands a large ezpease: A) The applicant shall fund the public notification efforts including public hearing notices to residenu and property owners within 3000 feet oC the proposed project boundary, legal and display advertisements in local newspapers and a paper of general circulation, and a sign (24 sq. Ct.) to be displayed on or near the project site (pursuant to the Government Code, Section 65090). B) The applicant shall be required to Cuad permit review activities pursuant to Government Code Section 65941.5 and the Health and Safety Code Section 25199.7. policies/Actions Reouired of this Jurisdiction • P/A-5-3 Because the County recognizes it's responsibility for siting needed specified hazardous waste facilities proposed in environmentally sound locations, this County will consider applications for specified hazardous waste facilities. Proposals to site such facilities in the County muss include applications for a Site Approval (Conditional Use Permit) and for a specified .Hazardous Waste Facility overlay (sec P/A-5-4). A decision on the applications will be based oa making the following findings: s. The proposed project is consistent with the provisions of the Development Codc (zoning ordinance), the CHWMP including the siting criteria, and the public resources code (Section 21000, et. seq.). b. The facility location and/or design adequately protect public health, safety, aad the environment. c. The project is proposed in an area where present and future surrounding uses are compatible with the specified hazardous waste facility. P/A-5-4 Because local land use plans snd zoning ordinances are required by state law to specifically address the permitting of specified hazardous waste facilities and sue6 plans sad ordinances do not address requiremenu for these facilities, sad because applicants • Cor specified hazardous waste facilities are required to apply 5-21 n LJ for a project-specific request to include the hazardous waste facility overlay on the project sitc and buffer zone and existing ordinances do act define or specify the requiremenu of such as overlay, this jurisdiction shall amend the Development Code (or 2.oaing Ordiaanee) to tegni'e all specified haardoas wasu facilities to be permitted oaly with to approved Siu Approval (Conditional Uu Permit) b areas with a zoning overlay of Specified Hazardous Waste Faeiliry. The overlay shall be applicable to all specified haurdous waste facility applications. The Durpou of the overlay is to ensure that facilities arc sited in areas that protect public health, safety, welfare, wad the environment; to suign the specified Hazardous Waste Facility overlay to the project site wad buffer so that incompatible uses cannot be permitted in the future; to identify permitted ttsa oC the overlay; and to outline the permit review procedures. The Development Code (or zoning ordinance) shall define the Specified A~rdous Waste Facility overlay as eontainiag the following: 1. A regniremeat that specified hazardous waste facilities may locate in certain bad use districts (or zone) with to approved Siu Approval (Conditional Uu Permit) and Specified Haardons Waste Facility Overby. Iaad disposal facilities wad ineineratioa facilities should locate in Resource Conservation Districts (or zone) with as approved Specified Hazardous Waste Facility Overlay. Treatment, _ ~'; iaciaeratioa, recycling, storage, wad tnnzfer facilities should locate is Regional Industrial districts (heavy industrial zone or equivalent) with an approved Specified Hazardous Waste Facility Overlay. Iaeiacratioa facilities shall ,not, however, be located in areas where emissions from the facility could directly impact food crops or livestock. (See diseussioa in Section 53.1 oC this chapter.) 2 The siting criteria presented in this chapter (starting on page 5-2E). The criteria shall be adopted as development standards that shall be mct along with provisions of the Development Code ~(soning ordinance) before a facility is approved Compliance with the siting criteria shall be evaluated at the time oC permitting. . 3. The app[ieation procedures wet out in AB 294E (Chapter 1504. Statutes of 19g6) for the review of specified haardotu waste faeiliry appliations. 4. A requirement that all specified hazardous wore facility appIieatioas are subject to a Speeb! Use Permit with a copy of the disclosure statement required by Health wad Safety Code Section 25200.4. The purpou of the Special • Uu Penait shall be to evaluate the opentioa and 5-22 • monitoring plan of the facility, to ensure the facility has adequate measures for monitoring on-going impacts [o air quality, groundwater, and environmentally sensitive resources, to evaluate the types and quantities of wastes that will be treated or disposed of at the facility, and to require periodic inspections of the facility to ensure conditions of approval are carried out S. A requirement that all specified ~ardous waste facility appIiations include information about the project proponent's past business practices with a coDY of the disclosare atttemeat rcgnired by Health sad Safety Code Section 25200.4. 6. Dizerctionary application review requiremenu to ensure developers are aware of the different studies that will be required in the environmental analysis when assessing the merit oC facility applications. A reporting and monitoring program shall be adopted to mitigate or avoid significant environmental impacts as required by AB 3180 (Chapter 1232, Statutes of 1988). The different issues that must be studied consist oC, but are not limited to, the following: a) An analysis oC the project's potential impact to surface and groundwater resources as well as public • water. SuDDliei The study shall identify monitoring sad mitigation measures that ensure protection of vital surface and groundwater resources for the life oC the project b) An evaluation of the project's impact to air quality and the consistency of the project with air quality regulations and the local air quality plans. The evaluation must consider tozie air contaminants, wind patterns, and an assessment oC the project's impact to PSD and non-attainment areas. e) An analysis of potential mineral deposits through a site characterization study. d) A review of the adequacy and capacity of the proposed transportation routes including an identification oC highway accident rates. (Refer to Chapter 10, P/A-10.3, Cor other issues to address in the study.) e) An assessment of risk on the population that evaluates the physical and chemical characteristics of the specific types of wastes which will be handled, the design features of the facility, an evaluation of potential air emissions from proposed facility, and • 5-23 any need for buffers from residences, immobile • populations, and environmeaully sensitive resources. f) If a facility proposes to handle acutely haurdous waste, an analysis of the maximum credible accident may be aeeesury pursuant to AB 3777 (Chapter 1260, Sutures of 19g6). The study shall uke into consideration the quantity and types of wastes that could be receivcd at the facility, the design features, sad the planned operational practices at the facility. Sased on the above items, the study shall provide an estimate of the disuaee over which any effects would carry, options for reducing the risk, and procedures for dealing with the effects, including recommendations Cor an appropriate buffer disunx. g) An evaluation of cultural, archaeological, and paleontological resources on the project site and surrounding buffer. P/A•5.5 Becausc several agencies (i.e. Air Quality agencies, Regional Water Quality Control Board, Dcpartmeat of licalth Services) and local governments (County, cities sad Special Districts) will be involved in the permitting of specifiedhazardous wsstc facilities, this jurisdiction shall request all applicable agencies • sad local government dcpartmcats to participate in a meeting of a specified 6aardous waste facility application at the prc• application stage (u required by Acalth and Safety Code, Section 25199.7 (e)). The purpose of the meeting is to ducuu and documcnt issues of concern to all app*opriate agencies u well as application review requirements tad time frames. This jurisdiction will assist the applicant in developing a matrix oC all reviewing ageaeiu and agency requirements before a formal application is accepted. P/A-5-6 Because specified haurdous waste facilities have a potential Cor adverse impacts on the environment, all aDpiications shall comply with the policies of the Cliti7vlP and the siting criteria antl shaft be the subject of environmental analysis. The eaviroamenul analysis shall be done as a consolidated effort among applicable Couary Departments. Compliance with the siting criteria shall be evaluated in the eaviroamenul analysis. P/A-5.7 Beeauu a sigaifitxnt portion of County land falls under federal jurisdiction, the Bureau of Land Managcmeat (BLAB, US. Forest Service, and the Dcpartmeat oC Defense (DOD), and the policies of DOD exclude the development of specified hazardous waste facilities, sad becauu ladian lands comprise another signifieaat component sad Native American Tribal Councils have expressed • concern over the development of specified hazardous waste 5-24 ' • facilities in the County, the County shall take the following actions: A. Complete a Memorandum of Understanding with the Bureau oC Laad Management (BLM) regarding review of specified hazardous waste applications Cor those projeeu proposed on land owned by the BLM; B. Notify and request involvement of Native American Tribal Councils in the review of all specified hazardous waste facility applications in their region; and C. Low-volume transfer and storage facilities may be located on private lands in the Death Valley and Joshua Tree National Monumenu, Mitchell Caverns Slate Park, National Forest Lands administered by the US. Forest Service, the East Mojave National Scenic Area, and any Wilderness Area designated by the US. Department oC Agriculture, or wilderness study area designated by BLM as suitable for a Wilderness Area pursuant to the Federal Land Management Policy Act oC 1976 if necessary to handle wastes generated by visitors, workers, or residents in these areas. When Congreu acts on Wilderness Areas this policy shall be amended to be consistent with those Wilderness Areas. • Other facilities should not be allowed in these areas. P/A-5-8 Because start law authorizes s tax (not exceeding 10% oC gross receipu) oa as approved specified hazardous waste facility, and these facilities have a potential to impact the environment, public health, and public services, this jurisdiction shall set aside a portion of the revenue Cor programs that encourage safe and responsible management oC hazardous waste. P/A•5-9 Because the siting criteria and the policies oC this plan should be applied uniformly throughout the County in order to ensure that effective management oC hazardous waste and that facilities are sited only in environmentally sound locations, the County shall encourage all the cities within the County to adopt the CHWMP and the siting criteria and development policies. P/A-5-10 Because specified hazardous waste lacility proposals could impact proposed city or County redevelopment projects, this jurisdiction shall inform the applicable redevelopment agency o! all specified hazardous w:ste facility applications. P/A-5-I1 Because the CHWMP seu forth comprehensive criteria Cor siting needed specified hazardous waste facilities, the airing criteria should be used to determine the suitability of projects in all County, city, start, and federal lands. • P/A-S-]2 Because the Department of Defense (DOD) contributes significantly to hazardous waste production is the County as a 5-25 ~ ~ result of site nmediation efforts, DOD opentioas, and businesses e producing products for DOD, this plan encourages the following: A) That the DOD implement waste reduction efforu to the maximum extent possible. B) That the DOD obtain appropriate permits from local jurisdictions aad allow periodic inspection of facilities for compliance with eavironmeaal regulations. C) That the DOD consider nndertakiag land exchange or lease agreements with industry desiring to site specified hazardous waste facilities is DOD property. D) That the DOD undertake hazardous waste management efforts which are consistent with the goals and policies/actions of this Plaa. P/A-5-13 Because cement kilns can use certain hazardous wastes as a secondary fuel and the use of such fuel significantly reduea kargc amounts of waste and may result is improved air emissions, this jurisdiction shall encourage facilities in San Bernardino County with cement kilns to uu certain hazardous wastes as - alternative sources oC energy, only where improvements in air emissions can be achieved. • P/A-5-14 Because Section 65300 of the California Government Code places a dual mandate on how cities and counties must consider development within a sphere of intlueax, the County shall ensure that all appiieations for specified haurdous wsstc facilities are reviewed for consistency with the goals and policies of the 1989 County General Plaa regarding development is a sphere of influence (LU-8 and LU-9). P/A-5-15 Because San Bernardino County obtains about 85% of its drinking water from groundwater and a significant percentage of the population of Southern California also depends on San Bernardino County groundwater for its beneficial uses, and because inappropriately sited development (inelydi•~g i~eci:-led hazardous wastc facilities) have the potential to adversely impact groundwater, this jurisdiction shall develop a County-wide groundwater protection strategy. The strategy should consider specific policies aad programs for regulation oC potential sources of pollution as welt as identify mechanisms to detect and correct possible impacts to the groundwater. r~ ~~ • 5-26 • SITING CRITERIA FOR SPECIFIED HAZARDOUS WASTE FACILITIES (Refer to Policies P/A-5-4 AND P/A-5-6) 1. PROX17vIITY TO RESIDENCES a. A 2000 foot buffer zonc from residences shall be required for the permitting oC any hazardous waste residual reeositerv unless the owner demonstrates to the satisfaction of the State Department of Health Services that a buffer zone of less than 2000 feet is adequate for the protection oC public health and safety. To determine the appropriate buffer a risk assessment shall be required which considers the physical and chemical characteristics of the specific type oC wastes that will be handled, the design features oC the facility, and any aced Cor buffering residential areas or other sensitive areas Crom adverse emissions from a proposed facility. _ b. A risk assessment shall be rcquired when permitting any treatment. recvelina. storage. and tranefcr faeilitie~. The risk • assessment should consider the physical and chemical characteristic of the apeeiCie type of wastes that will be handled, the design oC the facility, and any need for buffering residential areas or other sensitive areas from potential accidents or adverse emissions from a proposed facility. 2 PROX11vQTY TO DvOriOBILE POPULATIONS Soeeified hazardous waste facilities Shall be sited so that no significant risk is presented to the immobile population. Aa adequate buffer between the haurdous waste facility and the immobile population shall be established by s risk sssessmcnt at the time of permitting. The risk assessmcnt shall consider the physical and chemical ~turaeteristics of the specific types of wastes which will be handled and the design features of the facility and proximity to immobile populations. Immobile populations include schools, hospitals, convalesces[ homes, prison facilities, facilities for the mentally ill, etc. 3. PROXDrIITY TO PUBLIC FACILTfIFS $peeified hazardous waste faeitiues should be sited in such a manner as they do not adversely impact the public health cad safety of large numbers oC people in public areas or people in public facilities. An adequate buffer shall be determined by a risk assessment at the • time of permitting. 5-27 4. PROVISION OF PUBLIC SERVICES • Soeeified hazardous waste facilities should be located in areas where emergency response capabilities and public water and sewer services are available. When facilities are -oeated is desert or rural areas where public services are not readily available, privatelywwned onsite water, ewer. and emergency services (self-sufficient services) may be used. 5. FLOOD PLAIN AREAS a. Residual repositories may be looted in areas subject to 100• year events provided such facilities meet the requirements of the RWQCB pursuant to CCR, Title 23, Subchapter 15, Settioa 2531. b. Treatment. recvciinc_ storage- and transfer facilities may be located in areas subject to 100-year flooding if designed, constructed, operated, and maintained to prevent failure due to such events flood plain areas include areas subject to flooding by dam or levee failure and natural causes such as river . flooding, rainfall or snowmelt, tsunamis, seiehes and eosstal • flooding. ,; 6. PROXIIv1ITY TO ACTIVE OR RECENTLY ACTIVE FAULTS No Soeeified hazardous waste facility should be placed within 200 feet oC an active or recently attive fault. (California Code of Regulations (CCR),.Title 22, Section 66391 (a) (11) A (1) and (2).- UNSTABLE SOILS s. Residual Reeosirerv shalt not be located in areas of potential rapid geologic ehaage (Title 23, Subchapter 15, -- of the CCR). b. Treatment- reeveline- steraae- and transfer facilities may be located in areas oC potential rapid geologic ehaage if designed, constructed, mainuined, and operated to prevent failure ss a result of such changes (Title 23, Subchapter 15, Section 2531 (e) of the CCR). n U 5-28 „ • PROTECT GROLt-at~WA'r't=tr nrTar trv g. DEPTH TO GROUNDWATER a. Residual Reeositorv shall be located in areas which meet the requiremeau oC (Title 23, Subchapter 15, Section 2531 (a) of the CCR) and which meet the siting requirements of the State Water Resources Control Board. b. Treatment reevclin¢. stora¢e and transfe fa iliti may be located to high groundwater areas if engineered design of the containment structure is capable of withstanding failure because of geologic or soil failures which may arise. 9. MA]OR RECHARGE AREAS FOR AQUIFERS a. Residual Reeositorv should be prohibited within any area known or suspected to be supplying principal recharge to a regional aquifer is dcfined in state, regional, or general plans b. Treatment. reevdin¢- stora¢e and tran~f~r fa iliti a may be located to principal recharge areas iC facilities are designed, constructed, maintained, and operated to prevent accidental releases • 10. PERMEABILITY OF SURFICiAL MATERIALS s. Residual Reeositorv shall be located in areas where underlying geology provides .impermeability meeting the requiremeau of the SWRCB (pursuant to Title 23, Subchapter 15, Seetioo 2531 (b) (1) of the Cafifornis Codc of Regulations). b. Treatment. _reevelin¢. stora¢e- and trart~fet faeifiti ~ may be sited is areas where soi-s are permeable if adequate engineered features such as spill containment, monitoring, and inspection measures are included in the project design and construction. 11. NON-ATTAINMENT AIR AREAS Specified hazardous waste facilities may be located in non-attainment areas if the Caeilitia meet the plans and regulations of the air quality agency of each district, and a risk assessment shows that this contribution is sot signifitxat when compared to the emissions from transportation of hazardous waste out of this area. • 5-29 12 CRITERIA POLLUTANTS 1T7 PREVENTION OF SIGNIFICANT • DETERIORATION (PSD) AREAS Specified hazardous waste facilities may be located in PSD areas if facilities meet the pleas and regulations of the sir quality agency oC each district. These facilities, however, may not be located sear or within national parks, wilderness and memorial areas, and other similarly dedicated areas, as specified in the Clean Air A¢L 13. WETLANDS Soeeified hazardous waste facilities shall be prohibited Crom impairing the viability of wetlands such as saltwater, fresh water, and brackish marshes, swamps, and bogs inundated by surface or groundwater with a frequency to support, under normal circumstances, prevalence of vegetative or aquatic lift which requires saturated soil conditions for growth and reproduction, as defined is general, regions!, state, and federal pleas. A protective buffer zone shall be established based on a biological resource study and risk aszessment conducted at the time of permitting. • 14. HABITATS OF THREATENED, RARE, OR ENDANGERED SPECIES Cnecified hazardous waste facilities shall be prohibited From impairing the viability of critical babiuts oC tbreateaed, rare, or endangered species as defined in general, regional, smote, and federal plans. A protective buffer zone shall be established based on a biological resource study and risk assessment conducted at the time of permitting. 15. PRIME AGRICULTURAL LANDS Soeeified hazardous waste facilities may not be sited on prime agricultural lands as defined in California law and adopted local land use plans unless an overriding public aced is nerved. When siting hazardous waste management facilities in tbese areas, overriding public service needs must be demonstrated. 16. RECREATIONAL, CULTURAL. OR AFSTFIECIC RESOURCES Soeeified hazardous waste facilities shall not be located in recreational, cultnrtl, or aesthetic resource areas except low volume transfer and storage facilities which arc necessary to handle hazardous • waste generated by visitors, workers, or residents is these areas. 5-30 • Recreational, cultural, and aesthetic resource areas include public andlor private ]ands having local, regional, state, or national significance, value or importance such as: national, state, regional county and local parks and recreation areas; historic resources; wild and scenic rivers; scenic highways; ecological preserves; public and private preservation areas; and other lands of local, regional, state, or nationalsignificanee. 17. AREAS OF POTENTIAL MINERAL DEPOSITS Soeeified hazardous waste faciliti ~ should not be located so as to preclude extraction of minerals necessary to sustain the economy of the State. LAND USE RESTRTCTION l8. MILITARY LANDS Public specified hazardous waste facilities shall not be sited on military lands pursuant to DOD policy. ENSURE SAFE TRAN PORTATION OF HAZARDO WACTF • ' 19. PROXIMITY TO AREAS OF WASTE GENERATION a. Land disposal facilities may be located more distant from waste generation sources than other facilities because of their requirement for larger land and buffer areas. b. Treatment. reevcline. storaee. and transfer facilities should be close to hazardous waste generation sources to minimize the risks of transportation. 20. PROXIMITY TO MAJOR TRANSPORTATION ROUTES Soeeified hazardous waste facilities should have good access to and from major transportation routes. 21. MINIMIZE TRANSPORT THROUGH MINOR ROUTES Soeeified hazardous waste facilities should be sited so that road networks leading to major transportation routes do not pass through residential neighborhoods, should minimize residential frontages, and should be demonstrated to be safe with regard to road design and construction, accident rates, excessive traffic, etc. 5-31 REFERENCES • CHAPTER 5 -SITING OF SPECIFIED HAZARDOUS WASTE FACiI.ITIES 1. California Department of Health Services, 1987. Guidelines for ~ecaration of Hazardous Wastc Management Plans and Technical Reference Manual. 2. California Department of Health Services, 1986. Alterna tive Teehnoloav for Recvel ine and Treatment of Hazardous Waste. Third Biennial Report. 3. California Guidelines. Office oC Planning and Research, 1987. General Plan 4. California Office of Planning and Research, 1987, Guidelines for Shine S~ee ified Hazardous Waste Facilities Under AB 2948. 5. New York State Legislative Commission of Tozie Substances and Hazardous Kiln Oratio Wastes, 1987. Hazardous Waste Incineratio n. n: The Cement 6. Southern California Hazardous Waste Management Project, 1985. Hazardous Waste Facilities Sitine Manual. • 5-32 • • CHAPTER6 GENERAL REQUIREMENTS FOR HANDLING AND STORAGE OF HAZARDOUS MATERIALS 6.1 INTRODUCTION In the early 80's, leaking underground storage tanks began to receive widespread publicity because the hazardous materials contained in these tanks caused groundwater contamination and other environmental concerns. These events occurred in local areas such as Santa Clara County in Northern California, as well as other areas of the Country like New York State. The recognition oC the potential problems associated with underground storage of hazardous materials in unprotected single wall tanks led to the adoption of a County ordinance in 1983. The County ordinance predated the state rcquirements, thus, the County retained authority in monitoring the safety of underground storage of hazardous material. As required by state law, the County program is as stringent as the state program. Federal legislation (Superfund Amendments and Reauthorization Aet of 1986) has also been adopted to mandate similar standards. Both the state and County programs must be as stringent as the federal program. State and federal governments have established programs which require • businesses that handle hazardous substances to prepare an inventory of the hazardous substances stored and to provide that list to a local agency designated to administer the program. The purpose of these disclosure laws is to have information available to first responders in the event of an emergency at the site and to provide information to local residents regarding the kinds and amounts of chemicals stored in their communities. This legislation, however, did not include standards for above ground storage of hazardous substances as part of its mandate. 6.2 DISCLOSURE REQUIREMENTS Assembly Bill 2185 (Chapter 1167, Statutes of 1986) mandates that all businesses handling hazardous substances provide to the local administering agency an inventory and location of hazardous substances stored on the property. This information must be provided in the Corm of a Business Plan. Table 6-I lists the information required to be submitted as part of a Business Plan. This law applies to all businesses which handle at any one time more than 500 pounds, 55 gallons, or 200 cubic feet (compressed gas) of a hazardous material. The Department of Environmental Health Services (DEHS) has been designated the administering agency for purposes of the AB 2185 program for the County of San Bernardino, including the incorporated cities (California Health and Safety Code, Division 20, Chapter 6.95). Funding for this program is obtained from permit fees levied against the hazardous . material handler. Local businesses in the County are notified in writing of the requirements of this program. Each business must submit its plan • 6-1 in triplicate. .The DEHS, the law enforcement agency, and the fire • department in which the business is located all receive copies. Information -- about these plans is available to the public during regular business hours. Efforts have begun to create a comprehensive data base management system accessible to DEHS. The automated data system would provide information about each hazardous material handler; the information would be taken from Business Plans. Assembly Bill 2189 (Chapter ]585, Statutes of 1988) merged the local requirements of the federal SARA Title III program with the AB 2185 program. This merge will provide some relief to businesses in complying with regulations. 63 NOTIFICATION OF UPSET With increased efforts to minimize and/or recycle wastes, some hazardous waste generators may incorporate new procedures into their manufacturing process which would significantly reduce their waste. These procedures -- are considered in-process systems because the hazardous material is treated or recycled as part of the manufacturing process. Thus, the material does not leave the manufacturing process, it is re-used resulting in a substantially lower generation of hazardous waste or, in some instances, no generation of hazardous .waste. IC hazardous waste is no longer generated these generators would not undergo routine generator inspections. • In the event of upset of this in-process equipment, measures must be taken to ensure proper management of hazardous substances that could be accidentally released into the environment. To ensure that adequate management takes place, DENS should be informed when nay upset (or malfunction) of this equipment occurs which results in the generation oC hazardous waste. State law now requires that all hazardous materials handlers notify proper authorities when an unauthorized release occurs. TABLE 6-1 KEY ELEMENTS OF THE BUSINESS PLAN • Inventory of each chemical handled (amounts and concentrations of each material as well as information on how and where handled.) • Name and 24 hour phone number of emergency coordinator. • List and location of emergency response equipment on site. • Emergency response procedures to be followed in event of a release. • Facility evacuation plan. • Persons within facility necessary to respond to a release. • Procedures Cor coordination with local emergency response organizations. • Material Safety Data Sheets • b.2 _ • 6.4 UNDERGROUND STORAGE REQUIREMENTS The DEHS is the administering agency for the underground storage tank program in the unincorporated areas as well as the incorporated cities. Underground storage must be regulated to prevent contamination due to chemicals leaking from either the tanks or auxiliary piping. In the event of such a leak, monitoring devices or practices should detect the leak at the earliest possible time so as to minimize any contamination which may occur. The underground storage program requires owners of tanks containing hazardous substances to notify the State Water Resources Control Soard of existing teaks and obtain a permit from the DEHS for existing tanks. A hazardous substance is defined as a chemical listed by the Director oC the Department oC Industrial Relations pursuant to Section 6382 oC the Labor Code, or as defined in the California Health and Safety Code, Section 25316, or as classified by the National Fire Protection Association (NFPA) as a flammable liquid or a class II or class III(a) combustible liquid. Owners must apply for a permit and plan review prior to installation of new tanks. An approved monitoring program must be carried out oa all tanks, new and existing. The Table 6-2 on the next page shows the range oC alternative monitoring procedure options possible for monitoring existing tanks. The options depend on the material in the tank and the depth to ground water at the site. The monitoring procedures allowed under the County ordinance differ from those identified in State law. The County set more stringent monitoring requirements for teaks located in environmentally sensitive areas, areas where groundwater is at certain depths, and in the mountain areas. If groundwater is between 0 to 30 feet at the tank location, groundwater monitoring is required. For tanks located where groundwater is between 30 to 100 Ceet from the surface or is the mountains, vadose zone monitoring is required. In areas where groundwater is greater than 100 feet and no other environmental risks exist then tanks can be monitored using daily inventory reconciliation, tine leak detection, and a yearly precision test. IC an in-tank automatic level device- is used then a precision test is only required every five years. Additionally, the operator must submit a quarterly report on inventory reconciliation. The Uniform Environmental Health Code requires that every underground storage tank within its jurisdiction be inspected once every three years pursuant to state law. Additionally, the owner/operator must file as annual report detailing any changes in the usage oC the tank. Closure of an underground storage tank requires permit approval and as inspection at. the time of removal. This requirement provides a means of verifying that no soil contamination has taken place. Funding for this regulatory program is derived from permit fees and plan check fees levied against the owners/operators of the underground storage tank. • Unauthorized releases from an underground storage teak are required to be reported to the DEHS. Oversight for clean-up oC leaking underground storage tanks is a joint responsibility oC the DEHS and the appropriate 6-3 N ~_ ~I L Y Z ~ ~ ~ u Z "' ~~ r ~ N c z c - ~ o c '~ ~_ r iY _ _ ~ i E i L ~ ! :70i ~ t ~ T ~ t i i[ i::~ } € ~ = t .fs = .~ ~S ~ :. - : , . l:.. ~.~ _ Y ~ F C _ _ ... C ~ ~ V ~ • • _ ~ ~ •wE t ~ i t ; t ~' i = _ _ i" ~i i ~-e .., ~ c ! _ R ~t t ~ = ~ i I 1 ~S V i L E ' = ~' ~ - ~ ~ ~ E E ` ~~F i~ p3' s i!• =ic i ~=~ : ~ s ~ _ ~ ~ ° ~ ~ ~ ~ ~ = 'i ! i i E . . : = p ~t ~ s -~ ~ d ~ ! ~! i y a 'E S. _`~ ~ ~ E~~ • ~ V 1 • = ~ - ~ - ~ t ~ ~~ ~~ ~ ~ ~ ~ ~ E -, ~ ~ ~~~ _'= ~' ~ i lei ~~ t ~ I ~ N t'1 I Q ~ m ~ m ( ~ O ~ " .. d , • ., 0 n V N CJ f ~_ • Regional Water Quality Control Board (RWQCB). The DENS assumes a lead agency role when soils are contaminated, while the RWQCB assumes lead agency status when the groundwater is contaminated or threatened. The County is served by three Regional Water Quality Control Boards. 6.5 ABOVE GROUND STORAGE REQUIREMENTS While there has been considerable attention focused on the storage of hazardous substances in underground storage tanks, less attention has been paid to as equally threatening situation-the storage of hazardous substances in above ground tanks and containers. Enforceable storage standards for above ground storage are necessary to ensure hazardous materials pose minimal danger. Above ground containment has the potential to cause danger to workers or the environment, if improperly stored. A County ordinance establishing minimum storage standards for hazardous materials should be developed. The standards should address the type of containment, the length of storage, and the physical design of the storage area. 6.6 HOME OCCUPATION PERMITS At the present time, DEHS policy does not allow businesses permitted under a Home Occupation Permit to store hazardous materials in a residential area. This means that btisineues such as pest control. operators • and pool service companies are required to store their supplies in s commercial or industrial zone. Similar requirements arc enforced by the cities. 6.7 GOALS AND POLICIES/ACTIONS 6.7.1 Goals G-6-1 To redact the risks posed by the storage of hazardous substances is above ground tanks sad containers. G-6-2 To minimize the threat oC contamination of groundwater from leaking underground storage tanks containing hazardous materials. G-6-3 To minimize the threat to residential areas from the use of hazardous materials. 6.72 Policies/Actions P/A-6-1 Beesuse some waste reduction technologies significantly reduce or eliminate the amount of hazardous waste generated since they are a part of the manufacturing process, sad because the equipment for these technologies can malfunction causing the potential fora hazardous substance release, the County shalt amend Uniform Environmental Code to require all hazardous waste generators and hazardous material handlers to report any such equipment malfunction or upset which may cause hazardous waste to be generated. 6-5 P/A-6-2 Because above ground storage of hazardous materials may pose a threat to public health and safety and the environment wad County ordinance do not include ataadards for above ground storage, wad because all hazardous material handlers may not be easily identified, the County shall do the following: A. Revise Division 3 of the Uniform Envii•onmeatal Health Code to establish above ground storage standards for hazardous materials The ordinance shall include, but not be limited to, the following requirements: - secondary containment oC substances; - segregation of incompatible materials; _ - storage of hazardous substances restricted to an area with a surface impervious to the subsane; - methods to prevent run-off of rain water and/or collection of rain water if area is not covered; - fencing and/or other security of the area with adequate signs present to inform of the presence of hazardous materials; - emergency equipment to be stored onsite as appropriate (eg. proper absorbent to deal with s spill or an appropriate neutralizing agent); and - ~ • - minimum storage distances from adjacent land uses. B. Establish a system for identifying all handlers of h:zardous substances with such measnre as: - review of telephone directories and other business listings; - exchange of information with city code enforcement officers, local fire agencies, and city business license offices; wad - field surveys as necessary. C. Review periodically each place of business registered is the hazardous material handler program to verify the hazardous substance inventory on file and to advise the handler of safe storage practices. P/A-6-3 Because leaking underground storage tanks threaten groundwater resources, the County shall do the following: A. Amend the nadergrouad storage task ordinance to maintain its consistency with state and federal requirements B. Continue to enforce the Uniform Environmental Health Code by such measures as plan review and inspection of new task installations, inspection of existing tanks at least once every three years, tad inspection at all tank removals. 6-6 r1 LJ C. Maintain records of tank performance by reviewing on- going monitoring programs to evaluate whether enrrent requiremeau provide adequate protection, or whether areas with high groundwater (at 30 feet or less) require more stringent protection. D. Develop a Memorandum of Understanding (MOU) with etch of the three Regional Water Quality Control Boards which identifies the respective duties of the Water Board and the DEHS regarding oversight of mitigation efforts E. Prepare an annual report detailing the number of teaks under permit with the County, the nature of their contents, monitoring programs in use, the number oC facilities inspected, and a listing of sites where an unauthorised release has occurred and iu clean-up status. P/A-b-4 Because certain home occupations use and store hazardous materials and the use and storage of hazardous materials in residential areas may pose a threat to the public, this jurisdiction shalt continue to prohibit businesses under a Home Occupation Permit to store hazardous materials for commercial use in residential areas. Violations of this policy shall be • subject to enforcement action by the local jurisdiction and/or fire authority. Ia addition, the County shall coordinate with cities in developing a Iist of home occupations that use hazardous materials or generate hazardous waste within city jurisdictions. The list shall be distributed to city and county planning departments. 6-7 CHAPTER 7 REGULATORY PROGRAM FOR GENERATORS (Inelnding Trsasportcrs and new TSD Facilities) 7.1 INTRODUCTION The federal law governing hazardous waste management, the Resourx Conservation and Recovery Act (RCRA), originally exempted hazardous waste generators producing Tess than 1000 kg (2200 lbs) per month of hazardous waste from compliance with that law. The 1984 amendmenu to RCRA, (the Hazardous and Solid Waste Ameadmenu of 1.984, HSWA), lowered the exemption threshold so that busineues producing more than 100 kg (220 ibs) per month of hazardous waste are now subject to RCRA. California has taken a different approach. California has never had any threshold value for determining compliance with the hazardous waste management requiremenu. Aay business which produces a hazardous waste must manage that waste in accordance with state requiremenu regardless -- of the amount produced. Although many oC the California laws have been • in effect since the seventies, local enforcement of these laws began is 1983 with the MOU agreement. In September of .1983, the DEHS entered into a Memorandum oC Understanding (MOU) with the California Department of Health Services. Through this MOU, DEHS agreed to monitor sll businesses who generate or produce hazardous waste within the County to ensure that they comply with all state laws and regulations pertaining to the generation and management oC hazardous waste. 72 IDENTIFICATION OF HAZARDOUS WASTE GENERATORS Approximately 2100 businesses have been identified as generators of hazardous waste; these businesses are under permit with the DEHS. Of these, approximately 85 businesses or about 5% generate more than 1000 kg (2200 lbs) of hazardous waste per month. Although these 85 generators ., represent a small percentage of the total number of generators in the County, they produce about 57% or 24,577 tons of the hazardous waste shipped offsite Cor treatment or disposal, excluding oil and solvents. Generators that produce less than 1000 kg (2200 lbs) per month of hazardous waste are considered small quantity generators. Generators were identified by compiling lists of businesses likely to generate hazardous waste based on Standard Identification Classification Codes (SIC Codcs). All the identified businesses received a hazardous • waste generator application. The application requested information on the amounts and types of waste generated and provided background iaformatioa on the need for and purpose of the application. Some businesses completed 7-1 • s ~~ the application, while a large percentage indicated that they did not _ produce hazardous waste wad many simply did not respond. The DEHS verified each responu; those businesses which did not respond received a visit by DEHS. Through this process about 1500 generators were identified. Subsequent efforts to identify new and existing hazardous waste geaentors has taken several approaches. A •door•to-door sweep' was conducted in selected industrial areas, particularly in the valley portions of the County. Using this aDDroaeh, DENS Field inspectors covered large portions of the County and identified a significant number of generators. The DEHS has also worked cooperatively with the local fire agencies through occasional joint inspections cad by sharing and exchanging lists. Despite rhea efforu, the DEHS estimates that there may be as many as S00 more hazardous waste generator doing business within the County which the DEHS has yet to identify. (This does not necessarily mean they are not handling the waste properly, since many do recycle waste oil wad solvents as a matter of economics.) The process of identifying hazardous waste generator, particularly small quantity generator, was a lengthy, labor-intensive process. Many generators were not aware of the requiremenu wad did not realize they were subject to them. Generators are required to have sn approved permit from the DEHS. Fees are based on the number of employees. Thou generators that completely recycle now-halogenated hydrocarbon waste are eligible for substantially reduced permit fees. 73 BUSINESS LICENSES Many cities wad counties is California are beginning to use a busineu license application and renewal form as a screening tool Cor determining whether businesses handle hazardous materials and/or produce hazardous ~~aste. Communities which use the business license as a screening tool have found it successful because it applies to all businesses. At the present time Saa Bernardino County does not require a busineu license of firms operating in the unincorporated areas. However,- the cities within the County do require a busineu license. The format wad quuiions asked by each city varies wnsidenbly wad few screen for use oC haurdous materials. Information about busineues in the cities could be obtained through the business license program. The County has some limitations oa its ability to institute such a program, but can use a similar system Cor obtaining information retarding businesses in unincorporated areas. See policy P/A- 7-2 7.4 EDUCATIONAL ASSISTANCE The compliance program iaclndea a strong educational component in • addition to routine inspections. The DEHS has co-sponsored with the University of California, Riverside -Extension a number of one-day ,y ; 7-2 n LJ workshops on regulatory requiremenu for hazardous waste generators and a oneday conference on waste reduction. The DEHS also provides speakers on these subjects at meetings of busineu and trade associations. Additionally, the Department publishes a Hazardous Waste Generator's Handbook and a quarterly newsletter to assist generators is keeping informed of regulatory changes. At present the workshops have been conducted in the valley areas where the predominance of hazardous waste generators are located. Members of the public present at the Yucca Valley workshop expressed a strong interest in having similar workshops conducted in their area. Similarly there is a need for such programs in Victorville, Barstow, and Needles. 73 LDvQT'ED QUANTITY GENERATORS The DEHS estimates that about 200 to 300 limited quantity generators are in the County. Limited quantity generators are those generators who produce less than Cive gallons or fifty pounds oC hazardous waste per month. For the most part these are small businesses with only a Cew employees and may include jewelry shops, print shops, and small machine shops. As indicated earlier under California law, there is no lower threshold below which businesses are exempt from storage, transport, and disposal requirement. Any business which generates hazardous waste, regardless of amount, is subject to the requirements. Limited quantity generators are now required to obtain a permit from DEHS at a minimal cost. 7.6 DLSPOSAL ASSISTANCE Many reports and studies on small quantity generators (less than 1000 kg or 2200 lbs per month) identify a critical need Cor assistance with disposal of hazardous waste either through a local transfer station or through "milk-run' pick ups. California provides a permit variance to allow milk- run pick ups for waste oil, dry cleaner waste, and spent solveau for recycling. There are commercial operations which meet the needs of generators of waste oil, dry cleaner waste, and spent solvents. Other types oC waste which are not addressed include waste paint from contractors, small plating shop wastes, resin operations such as in the manufacture of spas and surfboards, and some circuit board operations. DEHS staff has considered the feasibility of expanding the existing household hazardous waste collection program to include generators who produce less than 100 kg (220 Ibs) per month of hazardous waste (the federal threshold Icvel). The County could consider two separate types oC operation: I) a eollectioa center that accepts waste brought in by the generator (less than five gallons or fifty pounds at any given time), or 2) the County could coordinate a 'milk-run,' via a commercial hauler, to pick up waste on a routine basis. • ~ The County does not want to be compete with private business, however. If private enterprise can fill the need, the County will not pursue such a 7-3 i • program. There is a proposal for a commercial hazardous waste transfer station. 7.7 GOALS AND POLICIES/ACTIONS 7.7.1 Goaht G-7-1 To ensure that all businesses in the County that use hazardous materials and generate hazardous waste properly manage these substances. G-7-2 To provide hazardous waste generators with the necessary tools to comply with existing regulations by continuing generator education and technical assistance efforts. G-7-3 To determine the need for and feasibility of providing disposal assistance to small quantity generators. 7.7.2 Policies/Actions P/A-7-I Because hazardous waste generators need a Dermit from DEHS and such a permit requirement ensures on-going compliance with regulations, and because not all hazardous waste generators have been identified in this County, this jurisdiction shall `'.~, continue its efforts to identify hazardous waste generators by using field surveys and instituting cooperative efforts with fire agencies to exchange information. P/A-7-2 Because a consistent method of identifying businesses that use sad generate hazardous substances must be is place, this jurisdiction shall use a business license (or similar requirement) and its annual renewal to determine whether businesses handle hazardous substances. This policy shall be implemented by the following actions: A. Development of an agreement with all incorporated cities within the County to ensure that questions regarding the use of hazardous materials and the generation of hazardous waste are included on both the city's business license application form and its business license renewal form. The information obtained'. from these questions shall be shared with the DEHS. B. Initiation oC a business license or similar requirement for the unincorporated portions of the County to be used for information retrieval purposes. Questions shall request information on the use of hazardous materials and the generation of hazardous waste. •, 7-d n LJ P/A-7-3 Because many hazardous waste generators are not aware of local, state, and federal requirements, and providing information about these requirements could ensure compliance with regulations, the DEHS hazardous waste compliance program shall continue to include a strong emphasis on educational assistance to hazardous waste gencrators. Every effort shall be made to make then programs accessible to all areas of the County. The following actions shall be taken to achieve this policy: A. DEHS shall continue to publish a quarterly newsletter providing the latest information on new Taws and regulations affecting hazardous waste generators. B. DEHS shall continue to publish and update the San Bernardino County Hazardous Waste Generator's Handbook which includes information on applicable regulations, contacts at other regulatory agencies, and resources such as the waste exchange, recyclers and haulers availabic to generators. C. DENS shall continue to sponsor workshops on regulatory compliance with an added effort to schedule conferences in the desert portion of the County. • P/A-7-4 Because hazardous waste generators have expressed an interest in having assistance with disposal of hazardous waste, this jurisdiction shall perform a detailed needs :ssessmeat and feasibility study for a transfer station and/or County coordination of hazardous waste pick up in all areas of the County. The study shall include consideration of the types of wastes needing management, opportunities for source reduction, recycling and treatment, and the likelihood of private enterprise meeting this need. It an unmet need is found, this jurisdiction shall determine the feasibiiity of providing that unmet need. • 7-5 CIiAPTER 8 LAND USE REQUIREMENTS FOR HAZARDOUS WASTE GENERATORS AND HAZARDOUS MATERIALS HANDLERS 8.1 INTRODUCTION Public concern exists regarding the potential threat to areas surrounding• businesses which use hazardous materials and generate hazardous wastes, particularly with regard to the distance of such businesses to residential and immobile populations as well as major drinking water aquifers. While land use or zoning regulations provide a mechanism Cor siting industrial and commercial development, the use of hazardous substances by existing businesses may not be considered when changes to land use or zoning are adopted or residential development is approved. Consequently, residential areas may be sited near these businesses (or vice versa). To address this concern, information on the amount and type of hazardous materials and wastes used by new or modified businesses should be part of the discretionary review process. Development standards for the review of new or modified businesses should also be established. A two stage approach is necessary for the proper siting of businesses • that use hazardous materials and generate hazardous waste. The tint consists of requiring preliminary information regarding hazardous materials and waste management practices at the time of application submission. The second requires that this preliminary information be documented as specified in state law through a completed business plan, waste minimization plan, and, if applicable, a Risk Management Prevention Program. These .plans would be completed .prior to final approval of the land use application. All businesses are subject to the requirement for these plans whether or not they are filing for a land use application. The purpose of this Chapter is to identify when this type oC information would be necessary for new or modified businesses and to identify other needed land use requirements. 8.2 LAND USE REQUIREMENTS The process for implementing land use standards and information requirements should be adopted county-wide. Cities are encouraged to adopt these requirements in order to provide a consistent evaluation of industrial and commercial development throughout the County. The County Department of Health Services (DEHS) contracts services to cities within the County. In order to receive input from the DEHS before a decision is made on a project, cities mey consider implementing a proceu Cor requesting input Crom DENS when an application is received. The DEHS could also provide valuable expertise for the review of existing businesses within city jurisdiction. • 8Z1 Preliminary Information Requirements and Needs for Standards Land use approval of a new business or modification oC an existing 8-1 r1 LJ business should include consideration of the amount and type of hazardous materials used and the amount sad type of waste generated, the business practices Cor management and reduction of these hazardous substances, sad emergency response procedures in the event of an accidental release. This information provides the necessary basis from which to determine the potential risk of such a business to surrounding areas as well as the need and feasibility of measures to redact potential impacts. Requiring this information as Dart of the land use application provide early consideration and review oC the proposed waste management practices. The purpose of this early preparation would be to suggest other waste management options and to address any equipment seeds for waste management as they relate to the proposed Drojeet and land use. Restrictions in terms of the location of certain types of businesses should also be established. These restrictions could include Iimitations on the location of businesses handling acutely hazardous materials or large quantities of hazardous materials. This limitation could be implemented by requiring discretionary review (Conditional Use Permit or Site Approval application) oC all businesses handling acutely hazardous materials or large quantities of hazardous materials/wastes. Another consideration could be to restrict development of businesses using large quantities of hazardous materials or acutely hazardous materials to heavy industrial zones in urban areas. In addition to the concern raised by a threatened accidental release of hazardous materials, there is also concern regarding possible effete from ; long-term low level exposure to toxic air contaminants. R'hiie the respective air districts operating in the County are working with the California Air Resources Board to minimize such threats, the process oC identifying toxic air eontaminanu and developing control measures for each one is very lengthy. It may be possible to minimize public exposure to low levels of tonic pollutants through the land use planning and zoning process: Local jurisdictions should also establish location standards applicable to the development of businesses that handle certain types or amounts of hazardous materials/wastes. The standards could address the issues identified in the siting criteria for specified hazardous waste facilities (see Chapter 5). The standards should be adopted by ordinance so that the public and businesses are aware of the requirements. 82.2 State Requirements State law requires the preparation oC a Business Plan and, if applicable, a Risk Management and Prevention Program. These plans provide some information necessary to make t decision on a project. A waste minimization plan that identifies proposed waste management and reduction efforts is also necessary Cor lead use review. The information requested as part of the land use review should form the basis for the completion oC these plena prior to final approval oC a proposed development • Generally, it is easier and more cost-effective to incorporate minor design changes at an early stage in the planning process. Early preparation of 8-2 • these plans could alert staff about the potential for a hazardous situation. An additional benefit oC early preparation is the DEHS can review business plans and identify businesses which are also subject to the Risk Management and Prevention Program requiremeau. These plans are briefly discussed below. Business Plan Any business that handles a hazardous material or hazardous waste in excess of 55 gallons, 300 pounds, or 200 cubic feet, unless the federal threshold is lower, must prepare a business plan. The Plan disclose the types and amounts of hazardous material/waste stored as well as the location and manner in which it is stored. In addition, the plan identifies emergency procedures, equipment, and contact personnel. It is required under the California Health and Safety Code (Division 20, Chapter 6.95, Sections 25500 - 25520) and the California Code of Regulations (Title 19, Chapter 2, Sections 2729 - 2734). See Chapter 6 for more detail on the contents and purpose oC the business plan. The business plan is generally not required at the land use permit stage, although, some of the information supplied as Dart oC the business Dlan would be helpful in the land use permit Drocess. Both the cities and the County should require the business plan prior to final approval oC any new or modified business. Waste Irfinimization Plan The Hazardous and Solid Waste Amendments (HSWA) of 1984 established the basis for a national policy that requires hazardous waste generators to reduce or eliminate hazardous waste (see Chapter 4). Generators must submit a report to the Environmental Protection Agency (EPA) and the California Department oC Health Services describing their efforu to reduce the volume and tonicity of hazardous waste. Questions regarding waste minimization practices are part of the local hazardous waste generator/hazardous material handler application from the DEHS. Gencrally, this information is obtained after a land use aDDroval of a new business or this information is considered Cor existing businesses. Information on waste minimization practices would be helpful during the review oC a land use application for a new or modified business. Since a waste minimization plan may undergo continuous changes throughout the land use review process, preliminary information is necessary at the timc a application is submitted in order to provide suggested changes or cgmments on the plan before it is finaliud. Risk Management and Prevention Program AB 3777 (Chapter 1260, Statutes oC 1986) establishes a state mandate to • minimize the risk posed by industrial handlers of acutely haurdous materials by requiring the preparation oC a Risk Management and Prevention Program (RMPP) for s11 new or modified businesses. This mandate applies to businesses which store, manufacture, or use these chemicals. The 8.3 requirement for a RMPP acknowledges the need to protect the public from uncontrolled releases or explosions oC hazardous materials. AB 3205 (Chapter I5, Statutes oC 1988) requires the preparation of a RMPP Cor businesses proposed within 1000 feet of a school. The bill specifies that after July 1, 1989 a certificate of occupancy cannot be issued unless this requirement is met The California Health snd Safety Code, Section 25531 et. seq., requires that after January 1, 1988, any sew or modified business in San Bernardino County handling acutely haurdous materials (AHMs) is amount greater than 55 gallons of liquid, 500 pounds of solid, or 200 cubic feet of a compressed gas shall submit a Risk Management and Prevention Program (RMPP) to the County DEHS. State law defines an acutely haurdous material as any chemical of the list prepared by EPA and clattified as an acutely tonic material according to the criteria set forth in the Chemical Emergency Preparedaeu Program Interim Guidance document oa November 1, 1985 sad any supplemental amendments to the document The list is published in 40 CFR part 355. Refer to Table 8-1 Cor an outline of the contents of the program. DEHS has begun a public education campaign to inform hazardous materials handlers of this requirement This campaign has included newspaper advertisemenu (both general display advertiscmenu sad -egal announcements), press releases, sad presentations to trade associations, business organiutions and fire agency personnel. An expanded public information effort will be necessary for planning agencies, building and safety depanmeats, and the real estate industry because they generally have the first contact with proponenu of new or modified businesses. TABLE E-1 ELEMENTS OF THE RISK MANAGEMENT PREPENTION PROGRAM • Assess a wont case release of an acutely haurdous material (AHMs). • Report the nature, age, and condition oC equipment used to headle AHMs including schedules for testing and maintenance. • Controls used to minimize the risk of an accident • Alarms and detection systems. • Auditing, inspection, and record-keeping programs to ensure that the management and prevention programs are carried out ;~ 8-4 83 GOALS AND POLICIES/ACTIONS The following goals and poiicies/actions require the adoption of regulations for the consideration of new or modified businesses using hazardous materials and generating hazardous waste. Lt3.1 Goal: G-8-I To ensure that businesses locating within the County incorporate available risk management and waste minimization practices into their operations. G-8-2 To minimize the risk of exposure to hazardous substances by the residential and immobile populations. 832 Policies/Actions P/A-B-I Because information regarding the amounts and types of hazardous materials used and hazardous waste generated are important factors to consider when siting new development or reviewing existing businesses, this jurisdiction shall: 1) Amend the Development Code (zoning ordinance) to: • e) require new businesses to submit detailed information regarding the amounts and types of hazardous materials used sad hazardous wastes generated, the business procedures implemented to manage these hazardous substances,' and the emergency procedures employed in the event of an accident. The applicant must demonstrate that the business operations are consistent with hazardous material/waste legislation. b) require new or modified businesses to complete a business plan, waste minimization plan, and, if applicable, a Risk Management and Prevention Program prior to final approval of a land use permit for a new business or modification of an existing business. The requirements specified is AB 3777 (Chapter 1260, Statutes oC 1986) and AB 3205 (Chapter I5, Statutes oC 1988) regarding the applicability oC the RMPP shall be identified in the amendment. The plans shall be submitted to the County DEHS for review and approval. 2) Expand outreach efforu to city and County planning agencies, city and County building and safety departments, and the real estate industry regarding new planning sad reporting requirements as welt as the identification of the • types of businesses which may be affected by these requirements. Such a program should include the development of brochures and flyers describing the 8-S rCquirements sad an identification of types of businesses which are likely to handle acutely hazardous materials. P/A-8-2 Because certain quantities of acutely hazardous materials could pose a threat to the public hcalth and ufety sad the environment, this jurisdiction shall amend the Development Code (zoning ordinance) to require a conditional use permit Cor all businesses or governmental facilities handling acutely heurdous materials in excess of SS gallons, S00 pounds, or 200 cubic Ceet. P/A-8-3 Because inappropriately sited industrial facilities pose a thrcat to the public, sad because zoning ordiaantxs do not identify quantity or uu limitations for hazardous material/waste, and identifying restrictions could address future concerns with the siting of industrial facilities handling hazardous material/route, this jurisdiction shall evaluate the feasibility of establishing siting criteria that identify the types and amounts of materials allowed within particular zoning designations. The study shall identify a list of chemicals and appropriate thresholds which would cause a business to be subject to specific land cast restrictions, recommend changes in the Development Code (zoning ordinance) for review of such industries, and identify the advantages and diudvantages of implcmeatiag such an . ordinance. 8-6 CHAPTER 9 HOUSEHOLD HAZARDOUS WASTE' 9.1 INTRODUCTION The consumer has ready access to countless household produeu that are, or contain, substances meeting the criteria oC a hazardous material: namely, a material that has inherent chemical properties that are corrosive, reactive, ignitable, or tonic. A hazardous material has properties that could pose a risk to public health and the environment. When used properly, these household products do not constitute a risk to health or the environment. When the unused portions of these products are no longer wanted, however, they become a household hazardous waste (HHW), and if improperly disposed, thcy become a HHW problem. Household products can be classified into Cive general groups: household cleaners, automotive products, home maintenance and improvement produeu, lawn and garden products, and miscellaneous items like batteries or pool chemicals (See Table 4-1). Thesc products are common household items. They arc often discarded improperly because most individuals do not • recognize their potential danger. Improper disposal of HHW may lead to injury to refuse collectors and equipment damage, and when disposed to land, HHW may contaminate soil or groundwater. Disposal to landfills, storm drains, sanitary sewer systems, and the grouad, as well as evaporation and storage of these products, can lead to human health and environmental concerns. 9.2_ EXISTING PROGRAM FOR COLLECTION In 1984 the County oC San Bernardino established a comprehensive program Cor addressing the HHW problem. The program began as a pilot project under a grant from the California Waste Resources Control Board. The study dealt with the feasibility of separating-HHW from the municipal waste stream and disposing oC it Droperly. The County opened two permanent collection centers in February, 1985 as part oC the grant project, one at the County Agricultural Commissioner's office in San Bernardino and the other at the Central Valley Fire Station in Fontana. Based on the success of the pilot program, the Board of Supervisors approved County funding to continue the program and subsequently approved funding to expand the program. • •Portions of this discussion have been takes directly from the County oC San Bernardino, Draft Solid Waste Management Plan, 1988. 9-I TABLE 9-I EXAMPLES OF HOUSEHOLD HAZARDOUS WASTESt L HOUSEHOLD CLEANERS Drain Openers Oven Cleaners Wood and Mctal Cleahers and Polishes Toilet Bowl Cleaners General Purpose Cleaaers Disiafectants IL AUTOMOTIVE PRODUCTS Oil and Fuel Additives Grease and Rust Solvents Carburetor and Fuel Injection Cleaners Air Conditioning Refrigerants Starter Fluids Lubricating Fluids Radiator Fluids and Additives Wanes, Polishes, and Cleaners Grease and Rust Solvenu Body Putty Transmission Additives IIL HOME MAINTENANCE AND IMPROVEMENT PRODUCTS Paint Thinaers Paint Strippers and Removers Adhesives Paiats Staias, Varnishes, sad Sealants TV. LAWN AND GARDEN PRODUCTS Herbicides Pesticides Fungicides and Wood Preservatives V. MISCELLANEOUS - Batteries - Fingernail Polish Removers - Pool Chemicals - Photo Processing Chemicals t Office of Solid Waste and Emergency Respoase - US. EPA, A October 1986. Note: Not all examples oC aay generic type shown above are hazardous products e.g., some oven cleaners are not hazardous. The hazard associated . with a specific product depends on its specific chemical coastitueats. i; 9-2 The County HHW management program includes: o Fivc permanent year-round collection centers. (Refer to Table 9-2 for the location of these centers.) o One-day collection programs called 'Round-UDS' in areas oC the County not served by the existing collection centers. o One-day publicity and collection 'events' to publicize and encourage the use of existing centers. o An on-going public education and information effort to increase public awareness of HHW issues and also provide educational materials to schools and interested groups. Funding for this program is based on a surcharge on solid waste disposed at County landfills (currently 5.25 per ton). This type of funding was established' consistent with Section 66798.5 of the Government Code. Additional funds are provided by the City oC Redlands through the municipal -andfill and from County Land Usc fees. The total funding available for this fiscal year (1988/89) is anticipated to be 5479,000. Thus far, user Cees or other charges have been unnecessary, but in the future may be considered if additional revenue is needed. 921 Amouau sod Types of Waste Collected Through the Prognm • The total volume of HHW collected (round-ups and 6 permanent collection sites, includes the Fontsna site) during the past fiscal year (1987-1988) totalled 11,711 gallons (approximately 47 .tons), an increase oC 65 percent from the previous year. Waste oil is the most common waste brought to round-ups and collection centers. During fiscal year 1987-1988, 50% of the total waste stream or 5,895 gallons of used oil was collected. Latex and oil base paint represented about 249b of the total waste stream. The County has been successful in recycling a significant amoun[ of the household hazardous waste collected through the Drogram. Of the 11,711 gallons of HHW collected during the 1987-1988 fiscal year, almost 9000 gallons of used oil, paint, and gasoline were recycled. For instance, latex paints were bulked in SS gallon drums Cor reprocessing and reuse, while, oil based paints and thinners were bulked for removal oC solvenu and then Cor incineration in a rotary-kiln cement plant as an alternative fuel stock. Waste oil was collected and picked up by an oil reeycler. Other recyclable wastes included batteries (about 76), compressed gases, and mercury. With the exception oC some drums of PCB-contaminated paints, about 7796 oC the wastes collected is 1987/1988 were recycled either as a secondary fuel source or as a usable product (i.e. latex paints, automotive batteries, mercury). Most of the remaining HHW, approximately 2440 gallons, consists of wastes that are not treated or recycled because there are no feasible opportunities for treatment or recycling. This waste was placed in drums • (i.e., labpacked) and sent to Class I landfills. The DENS is currently examining the feasibility of recycling antifreeze and solvenu, and treating the pesticides that normally are a large part of the total HHW collected. 9-3 the pesticides that normally area -arge part of the total HHW collected. Changing regulations on the landfilling of pertain wastes has increased the options for commercial treatment. Of the total amounts oC waste collected in fiscal year 1987-1988, about 37% or 4358 gallows of waste were collected through the one-day round- ups. Onc-day collection events or Round-Ups serve areas not covered by the permanent sites. There were aeven Round-Ups hcld during the 1987- 1988 fiscal year in the cities of Twentynioe Palms, Rancho Cucamonga, Ontario, Upland, Crestline, Needles, and Big Besr. A total of 529 households participated in the one-day collection events. At each of the Round-Ups held last year, a questionnaire was distributed requesting information about previous disposal methods, willingness to pay for service, and how the participants became aware oC the event. Out of the 529 participants, 35% stored the wastes previous to the event while 28% took the waste to a facility and 26% Dlaced the waste in the trash. These figures indicate that household collection evenu provide a valuable service to those areas not covered by the permanent collection centers because they offer a means for proper disposal of HHW. The vatue oC the program is further reflected is the large cumber of respondents (82%) that stated a willingness to pay for scrvicc. Another interesting point was that participaau had heard about the one- day event through articles in the newspaper (44%), the radio (28)%, flyers (20%), and mailers (17%). About 6% oC the participants had learned about the event through a friend. Based on these figures, it is clear that present out-reach efforts are gcaerating interest in the one-day evenu, but out-reach must continue in order to gain more widespread recognition oC propcr disposal methods. 9.2.2 Waste Excluded/Accepted The cotlcction program accepts only HHW; hazardous waste generated by industry or any commercial enterprise is excluded. Informative materials are distributed that identify the types and quantities of wastes that are not accepted as well as those not considered hazardous that could be safely disposed elsewhere. Wastes expressly excluded include: o rsdioactivc materials; o Dressurized gas eylinden; o infectious waste; o explosive material (including ammunition); and o shock sensitive materials. A list of the more common HHW is included in brochures wad other educational materials Drovided to the public. A complete list of the acceptable HHW is available from DEHS. The educational materials advise residents to apply the following rules before transporting HHW to the collection site. 9-4 TABLE 9-2 HOUSEHOLD HAZARDOUS WASTE COLLECTION CENTERS' Hours oC &llsi Dave Ooen Onention County Agricultural Monday-Friday 8 a.m. - 5 p.m. Commissioners Office San Bernardino Barstow Fire Saturday 9 a.m. - 2 p.m. Department Barstow Foothill Fire Saturday JO a.m. - 2 p.m. Department Ranch Cucamonga _ Redlands City First & Third 9 a.m. - 12:30 p.m. Yard Saturday of • Redlands each month Vietorville Sundays 9 s.m. - 4 p.m. Department Victorville 'The Center in Fontana was recently closed. 9-5 Store all HHW in iu original container; Ensure that each container is -Ices than 1 Callon or ~ II43iIIdi: and Do not exceed a total oC 50 Hounds. or 5 ¢allons of HHW per visit 9.2.3 Storase The collected HHW cannot be stored at a collection site without a storage permit or variance from the State Department oC Health Services. The San Bernardino Household Hazardous Waste Center has a permit to operate as a treatment and storage facility for one year. The other Cour sites have variances allowing them to store HHW up to 90 days. All of the recyclable wastes are brought to the San Bernardino facility for bulking and reeycIing. A1I collected waste is stored in containers that are labeled (poison, flammable, corrosive, irritant or oxidizer) in accordance with Titles 40 and 49 of the Code of Federal Regulations. Lab-packed wastes are filled with enough compatible absorbent material (e.g., clay base) per drum to contain any spilled_liquids and prevent damage to the individual enclosed containers. All containers used to transport waste meet DOT requirements, are tightly sealed, and have liners compatible with the waste. 9.2.4 Personnel DEHS staff (4 positions) provide overall coordination and operation of the program. A program coordinator oversees all public education efforts, provides oversight of the permanent centers, and coordinates the one-day collection events. Staff from the permanent collection sites provide support for the Round-Ups. These individuals donate their labor on an in-kind basis. Other DEHS personnel, the County Agricultural Commissioner, and Fire Department personnel provide support to the Round-UD events as well. Each permanent site is operated by its respective agency staff. The staff possess the expertise necessary to accept, presort, package, and manifest the collected HHW as well as onsite supervisory and public relations responsibilities. Training clinics arc held once every six months Cor all personnel working at collection sites (permanen[ centers or Round-Ups). Training sessions are also held prior to each Round-Up to review safety procedures, use of safety equipment, and packing procedures. 9.23 Transport Atl of the collected HHW is manifested and transported by registered haulers to either the permitted facility is San Bernardino or directly to another TSD facility. The County, as the generator, provides all appropriate vehicle placards and labels to transporters who do not already have them. ', • i. 9-6 9.2.6 Publicity and Education Programs The County publicizes its collection program through media campaigns that include: (1) articles and public notices in local papers; (2) radio and television announcements; (3) distribution oC posters, stickers and flyers; and (4) direct mail announcements (mailers). The campaigns are conducted primarily during the spring and Call to coincide with the customary home and garden cleaning periods and/or in conjunction with various events (e.g., Firc Prevention Week, National Poison Prevention Week) or scheduled "Round-Up' days. The County also promotes a rigorous public education program to increase public awareness of the potential dangers from unsafe use and disposal oC HHW. As part oC the education program the DENS provides brochures, booklets, slide shows, videos, and teaching packets to schools and political interest community or service groups. Teaching packets were supplied to over 250 schools during the spring of 1988. 9.3 PROGRAM EXPANSION With the location of only five permanent collection centers County- . wide, there are vast areas of the County which are not being fully served by this program. The increased popularity of these events has increased • the number of users to a point where storage size of the San Bernardino site may not be adequate. Since expansion of the program will require a major capital investment by the County, careful consideration should be given to how this program could be designed to best serve the needs of all residents. New permanent collection centers may be added to the program since the Round-Up events are very labor intensive. The Round-Up events require trained personnel to accept, sort, and package large amounts of waste for processing (recycling, treatment, or disposal) in a fixed amount oC time. More HHR' program staff will be necessary iC the round-ups continue at last years rate (seven in 1988) and new permanent centers are added. At the present time [here are several full-time budgeted positions available in the DEHS that could be used for this program. Alternative measures to expand the program should also be considered, however. The program should be expanded to include collection centers at landfills, enforcement efforts at landfills to discourage improper disposal, and continued public education efforts. Participation by the County Solid Waste Management Department is recommended. 93.1 Collection Centers in Local Landfills Household hazardous waste is frequently disposed oC at municipal landfills. Landfill operators can easily identify some wastes as hazardous. When landfill operators identify hazardous waste in a waste load, the operator • refers the resident to a County sponsored collection center. The collection centers receive a fair amount oC referral business from landfills and rubbish haulers, although records are not maintained on the amount of referrals or the material brought to a collection center. Given the use oC 9-7 municipal landfills Cor disposal of household hazardous waste, the placement of a household collection center at landfills may be a valid consideration. 93.2 Enforcement Program Many of the landfills located in the desert are operated on as honor system. No one regularly requests identification as to County residency or checks for the presence of hazardous waste is the load. (This issue was a major concern for Yucca Valley residents who attended s public workshop; this issue dominated the discussion that evening.) While landfills in the valley areas do have personnel present, no formal load check or exclusionary program exists to verify that only municipal trash and garbage is disposed. Measures are necessary to restrict unauthorized disposal of household hazardous waste at landfills. 933 Pubiie Education At the present time DEHS has an extensive public education program to inform the public about the dangers of improper disposal oC household hazardous waste, sad about the availability of the collection centers. This program includes public service advertisemenu in several local newspapers, distribution of flyers, posters and brochures about the program at fain, malls, community group meetings, and to school classrooms. Despite this intensive effort, only a small percentage of the population is aware of the program and it is clear that education must continue is order to reach a larger percentage oC the population. The County's HHW management program, perhaps, the most compietc and progressive program is the nation, collects about 3.1 percent of the estimated 1,605 tons of HHW generated annuaily.t it is unlikely that more than 3 percent of the public could be encouraged to participate in Round- Ups or to bring their HHW to the five permanent collection center without an extensive public involvement program. Consequently, the collection program will not, in and of itself, result in significant reductions in the quantities of HHW improperly disposed unless public participation and education efforts continue. • 't. . 2 Based on a HHW generation rate oC 73 pounds/year/household and an estimated 430,947 households in the County, the total amount of HHW generated per year is expected to be approximately 1,605 tons (DEHS 19g7). • Consequently, the volume of HHW collected through the program represents about 3.1 percent of the anticipated HHW generated. , 4-8 • 9.4 GOALS AND POLICIES/ACTIONS 9.4.1 Goaht G-9-1 To ensure the effective management and disposal of household hazardous waste County-wide. G-9-2 To prohibit unauthorized disposal of household hazardous waste in facilities that handle wastes. G-9-3 To inform the public about the need for proper disposal of household hazardous waste and to inform the public of the availability of the collection centers. 9.4.2 PoBeies/Actions P/A-9-1 Because recent studies at municipal landfills show evidence of contamination Crom hazardous wastes, this jurisdiction shall establish a strong enforcement program to prevent disposal of household hazardous waste in municipal refuse facilities. P/A-4.2 Because household hazardous waste is disposed at local landfills and because a strong enforcement program will detect sigaiCicant amounts of household hazardous waste, this jurisdiction shall • develop household hazardous waste diversion programs at all facilities where waste is handled, to properly manage these wastes. Whenever possible, collection centers should be established st appropriate faeilitia with public access. P/A-9-3 Because the capacity at colleetioa centers can not accommodate the seeds of the entire County and the diversion program will add to the amount of hazardous wastes requiring spccisl management, this jurisdiction shall addreu the County's needs is effectively managing household hazardous waste by establishing s larger transfer and processing facility. P/A-9-4 Because public education efforts have alerted the public about proper methods for disposal oC household hazardous waste as well as the availability oC household colleetioa centers, and because there is a need to continue these efforu for County- wide public awareness, this jurisdiction shall continue its comprehensive public education program. 9-9 • RF.F>rRENC>rs CHAPTER 9 -HOUSEHOLD HAZARDOUS WASTE 1) County of San Bernardino, Department of Environmental Health Serviees, Household Hazardees Wage Pro¢ram Yes in R ~:.w Fiscal Year 1987-1988. September 1988. 2) County of Saa Bernardino, Draft Solid Waste Management Plan 1988. 3) County oC Santa Barbara, Hazardoes Waste Managemeot P~sn. 1988. 4) OtCiee of Solid Waste and Emergency Response - U.S. EPA, A Survev October 1986. i 9-10 CHAPTER 10 TRANSPORTATION 10.1 INTRODUCTION Hazardous wastes and materials are transported daily into and through the County. Generally, transportation of these substances goes unnoticed until an accidental spill or release calls attention to the public safety hazard. While emergency response personnel are trained to respond to such incidents, local governments tea have a more active role in ensuring safe transportation of materials sad w:arcs. The purpose of this chapter is to discuss the local role in salt transportation of hazardous material/waste in the County and to identify policies/actions that address transportation concerns. Hazardous waste is transported by truck out of the County to treatment, recycling, and disposal facilities, and into the County from other areas for treatment. In 1986, San Beraerdino County exported about 41,000 tons of hazardous waste; hazardous waste imported into the County comprised about 9,000 tons. While no current estimates czist for transport of hazardous materials, national estimates suggest that transporation of • hazardous waste is relatively insignificeat compared to the amount oC hazardous materials transported. These hazardous materials become hazardous waste when spilled in the environment. For this reason, both hazardous waste and hazardous material transportation is discussed in this chapter. Diseuuing only the tnnspomtion of hazardous wastes would inadequately represent the current situation. 102 TRANSPORTATION REGULATIONS Federal and state agencies are responsible for the development and enforcement of the transportation regulations throughout the state. The following discussion summarizes the regulations pertaining to transportation of hazardous material/waste. 1021 Federal The Department of Transportation (DOT) establishes and enforces regulations for transportation of hazardous materials and wastes. These regulations include requiremenu for proper containment, marking, and placarding, ss well as the aced for shipping papers and reporting requirements for discharges (Code of Federal Regulations, Title 49). The Environmental Protection Ageaey (EPA) also has jurisdiction over the transportation of hazardous materials and wastes. EPA requiremenu are Cound in the Code of Federal Regulations, Title 40. The Resource Conservation and Recovery Aet (RCRA) specifies that regulations established • by the EPA must be consistent with those established by the DOT under the Hazardous Materials Transportation Act (HMTA). EPA established regulations concerning the transportation oC haurdous waste and adopted those requirements established by the DOT. Likewise, DOT adopted l0-1 n LJ requirements applicable to hazardous waste established by the EPA. In addition, the two agencies have collectively developed the Uniform Hazardous Waste Manifest, a form used to track the transport of haurdous waste Crom its generation to ultimate dispoul. The transport oC haurdous material and waste is tracked by two different methods. The generator supplies either method of documentation to the transporter. Haurdous materials transport requires the use oC shipping papers. Shipping papers identify the type oC material being transported, the haurd class, sad the amount of material being transported. Haurdous waste transport requires a Uniform Hazardous Wute Manifest, a form more detailed than the shipping papers used to track waste from the "cradle to grave' as established in RCRA. The Manifest identifies the type oC waste being transported, the identification number oC the substance, the haurd class, the amount of waste being transported, the name of the generator, and the final destination and disposition oC the waste. The Manifest, a multi-phase form, provides the generator and state agencies documentation on the movement of hazardous waste. The Manifest system also provides state and local agencies with information oa the final disposition of the haurdous waste and provides s base of information about the amounts and types of waste generated is the state. The regulations established by the DOT and EPA auign responsibilities to the generator sad the tnasporter in the shipment of haurdous • material/wutc. These regulations are enforceable by the EPA, DOT, and State officials. Both the generator sad the transporter are required to maintain records regarding the transportation of haurdous wastes Significant responsibility rests on the generator in ensuring proper handling oC haurdous wastes To ensure proper handling, the generator must prepare a haurdous waste Manifest (or shipping papers for haurdous materials), properly label, mark, and package the waste, use DOT specified containers, and use only registered transporters and permitted treatment, storage, or disposal facilities (TSDF). In addition, the generator must ensure that identification of the type of material/waste transported (termed placarding) is placed on the outside of the vehicle. The placard provides a quick indicator oC the vehicle's contents, and must conform to standards for color, size, and specific markings as outlined in the regulations (49 CFR 172, subpart F of .DOT regulations). Certain material/waste, except any material/waste considered "extremely haurdous', is exempt from placarding iC the cargo weighs less than 1,000 pounds A vehicle transporting any quantity of extremely hazardous material/waste, including empty container with residues, must be placarded. Extremely haurdous materials/wastes include: cerain explosives, certain radioactive substances, flammable solids, and various poisonous substances (49 CFR 172.504). The transporter also has responsibilities to see that materials/wastes are properly transported sad must be prepared to handle any potential • accidents. The transporter must verify that material/waste are placed in DOT specified containers, ensure the use of an adequate placard, comply .. lag with the Manifest system, and comply with DOT regulations pertaining to reporting of discharges or spills. 10.22 State The State has adopted the federal regulations pertaining to the transportation of hazardous materials and waste. The State Department oC Health Services (DHS) tracks the shipment of hazardous waste in the State through the uae of the federal Manifest system. The State requires a modified- Hazardous Waste Manifest Corm as provided under the Health and Safety Code, Section 25160 (c). California businesses should use only the Uniform Manifest issued by DHS (EPA Form 8700.22 DHS 8022-A). An exemption Crom the full manifest requirements has been provided for the transportation of limited quantities of household hazardous waste. The DHS also enforces the requirement for the waste hauler registration. The California Highway Patrol (CHP) cnforces hazardous waste and matcrials regulations with regard to transportation. The CHP periodically inspects vehicles carrying hazardous materials and waste under the authority of the California Vehicle Code, Section 32001. The CHP inspects the packaging of hazardous substances, placarding on the vehicle, and the condition of the vehicle. The CHP may inspect a vehicle at any time, without probable cause. In addition, the CHP Motor Carrior Specialists conduct annual inspections of transport vehicles to issue a certification as • required by the DHS. The vehicle certification is accessary for the waste hauler registration issued by DHS (Health and Safety Code, Section 25163 (a)(I )). 10.3 THE LOCAL ROLE Although federal and state agencies are responsible for the development and enforcement of transportation regulations, the local jurisdiction can have a role in the transportation of hazardous material/wastc in the County. The local jurisdiction may designate routes, restrict hours oC transportation, institute notification requirements for certain categories of waste, and provide educational and training opportunities in the transportation of hazardous material/waste. In addition, the local jurisdiction may implement road mitigation measures, such as repair oC roadways, to reduce the risk of transporting hazardous materials/wastes. Federal law preempts any state or local requirement which is inconsistent with the requirements of the Hazardous Materials Transportation Act (HMTA). A state or local requirement may not be preempted iC the DOT (or the courts) determines that the state or local requirement provides an equal or greater level of protection to the public than the federal requirement. Federal law specifies, however, that the state or local requirement cannot unreasonably burden commerce. 10.3.1 Route Designation • Vehicle Code, Section 31304 describes a process for local government to restrict or prohibit the transportation of hazardous materials and wastes. 10-3 The local jurisdiction may institute a restriction by local ordinance. The ordinance will be' upheld if it meeu the following conditions: 1. The restricted highway is appreciably left safc than a reasonable alternative highway as determined by either. a. The use of the 'Guidelines for Applying Criteria to Designate Routs for Transporting Haurdous Materials' prepared by the Federal Highway Administration (FHWA A-1-P-80-IS), b. The Gliforaia Highway Patrol or local jurisdiction determines the restricted highway is located within the watershed of a drinking water reservoir which meets certain requirements; 2. The restriction is not preempted by federal law; 3. The restriction does not eliminate access to pickup or delivery points, fuel, repairs, rest, or food facilities intended to accommodate commercial vehicles; 4. Written concurrence bas been obtained from surrounding jurisdictions; 5. The highway is properly posted; and 6. Notification is distributed to appropriate agencies and industry. To date, only three state highways have been restricted in Glifornia; Highway 154 in Santa Barbara County, and San Pablo Rosd and Bear Creek Road in Contra Costa County. All three of these routes were restricted from transport of haurdous material or waste because of their proximity to watersheds. In other parts of the Country, such as Dallas, Fort Worth, Columbus, Denver, and Boston, hturdous materials routing restrictions have also bees adopted. A US. Congress Office of Technology Assessment report states that local regulations found to be consistent with DOT regulations generally iacroased safety sad were enacted by a local government in consultation with neighboring jurisdictions. Thus, routing considerations should be addressed on a county-wide and regional basis. San Bernardino County has identified four specific routes of coacera regarding transportation of haurdous material/waste. These four routes include 1-15 through Gjon Pass, State Highway 62 in the desert, Highway 58 from Kern County line to Barstow, and Highway 71. These routes are of concern for the following reasons (refer to Figure 10.1 for the locations oC these highways): Interstate Highway 15 draws heavy traffic. Since it is a mountain pass route, weather conditions often cause the route to close and there is ao alternate route. In addition, it is the only direct route connecting Victorville and the surrounding areas with the valley portion of the County. • 10.4 n U Highway 62 draws heavy residential traffic. This route is not a divided road and has a number oC improved and unimproved access roads intersecting at various angles. Drainage is not improved in many areas and Clash flooding occurs. Areas of soft shoulder exist. The route; a major access for several communities, is fronted by commercial and residential uses. Presently there is no alternate route to this highway. Highway 58 draws heavy traffic and has a proportionately high accident rate. This highway is currently a major truck route Crom the southern end of the Central Valley to the east. It is not e divided road and does not have access control. Local traffic and access to fronting land uses compound the situation. Highway 71 is the sole access route to the Chino Hills and commercial areas. It is not a divided highway. Portions of the route parallel a major area oC unique ecology. Commuter and residential traffic is heavy. Highway 58 will undergo improvements, including an upgrade from atwo- lane to a four-lane highway. Currently, part of this route (Highway 58) is used for transport of rocket fuel. In order to ensure safe transport oC the material on these routes, proposed improvements to the highway • should be accelerated. Interstate Highway 15 is also scheduled for improvements. An interchange in Victorville and a realignment and connection to Highway 58 in Barstow are the proposed improvemenu. Preferred routes Cor transportation of hazardous material/waste are interstate and state divided highways which do not pass through residential areas. The routes discussed above could be used when routes are improved to handle heavy truck traffic and transport of hazardous substances. Also, these routes could be used for low-voiume transfer oC wastes in resort areas depending on the type and amount oC wastes that would be transported. r1 L_J I o-s Fz- ,.~...., .... - ; ' r . --~ • °. t ----~ ' ~ ., ~ ,: - ' = 1' ..., ; ~ ~ . r-- .~ ti ....~ i ~ ~ ~ i ~ ~ i ~ ~ r ~ ' '' i. . ~ .... ..ice ' ; ~ ~ % v ............... 1 >- E-^ Z V z 0 z Z d ~1 • i • • 10.32 Other Areas of Local Involvement A second area for local involvement is in establishing notification requirements. Generally, transporters are required to notify emergency responders of the shipment of extremely hazardous substances as a means of improving emergency response to accidental spills or releases. Many emergency responders believe that prior no[ice of shipments in itself does not help improve their ability to respond to an accident. Instead, transporters should• provide information regarding the type, amount, frequency, schedule, and routes used for transport of hazardous materials/wastes. This information would be useful to the emergency response team in planning training efforts and in selecting emergency equipment. Currently, the CHP is notified of rocket fuel transport. This is the only hazardous substance where a notification is provided. Local jurisdiction may also choose to restrict the hours of transport through the County by imposing curfews. Imposition oC a curfew should be done with the involvement of adjacent jurisdictions. Local governments can reduce traffic hazards by improving road conditions, or, on State highways working with State officials to establish priorities on the repair of state routes. Lastly, the local jurisdiction can provide information to generators on transportation regulations so they may contract with -- reDUtable transportation companies. • 10.4 RAIL TRANSPORT AND THE NEED FOR A COMPREHENSIVE STUDY Rail transport has received attention :s a potential mode of transportation for hazardous material/waste. The Southern California Hazardous Waste Management Project (SCHWMP) developed a study regarding the transport of hazardous waste by rail. The study found that such transport was feasible and that rail was superior for long distance transport. -A comprehensive study, however, specific to San Bernardino County would be necessary to more adequately evaluate the potential for rail transport in this County. Since three major transcontinental railroads serve San Bernardino County (Santa 'Fe, Union Paeifie, and Southern Pacific) the use of rail transportation should be assessed for hazardous material and waste transport. Approval of a specified hazardous waste facility in this County could substantially impact present traffic conditions. If a land disposal facility ~is developed, hazardous waste could be brought in from various Darts oC the state as well as the Southern California Region. A comprehensive transportation study would also serve to address transportation concerns associated with a specified hazardous waste facility application. The study would evaluate the risks associated with transporting hazardous materials and waste in and through the County as well as consider the feasibility of rail transport. One of the issues considered in the Draft Regional Mobility Plan (Southern California Association of Governments, • .1988) addresses the concern for movement of goods through the Southern California Region. The Plan emphasizes the need to explore 10-7 . ~: alternate route of transportation and to coordinate local regulations to • improve trucking. lOS GOALS AND POLICIES/ACTIONS The following goals aad policies/actions address the need to ensure safe transportation of hazardous waste through the County. 103.1 Goals ' G-l0-1 To ensure the safe transportation of haurdous materials and waste in and through San Bernardino County. IOS.Z Policies/Actions P/A-10-I Because safe transportation of hazardous waste is an important goal of existing state law and local jurisdictions, specified hazardous waste facilities shall use routes that can safely accommodate additional truck traffic, do not pass through residential areas, wad use interstate or state divided highways as major routes. P/A-10.2 Because local jurisdictions can have a role in the ufe transportation oC hazardous waste, this jurisdiction shall establish a task force whose purpose is to develop proposals Cor specifying routes for hazardous waste transport, identifying limitations for scheduling times of day wad days of the week, " ripe of wastes that eaa be transported, and the need for notification requirements. Also, the task force shall further asseu the routes oC concern (Highways Sg, 62, 71, and I-15). The task force shoald be composed oC members of the pubiie, . City, County, and regional transportation planners, emergency response personnel, and industry with expertise in transportation of hazardous substances. P/A-10-3 Because specified hazardous waste facilities must have aceeu to safe transportation routes, this jurisdiction shall require applicants for specified hazardous waste facilities to fund an analysis of transportation concerns (see policy action P/A-S- 4(6)(d) Chapter S). The transportation study shall provide a description and analysis of the projected volumes of haurdous waste transported into and through the County. The transportation task force identified in poIiey/action P/A-10.2 shall participate with local government staff in developing the scope of the study. The study shall include, but not be limited to: Aa identification of all reasonably available highway wad railway routes in the Southern California region and the • development and comparison oC the risk associated with the alternate routes; 10.8 • A comparison of the risk auociated with transporting hazardous waste in different truck and rail cargo tanks; • An identification of route-specific, risk-reducing measures for each route examined; and • An identification and evaluation oC procedural (i.e., training, routing, curfews), technological (i.c., equipment innovation), and external risk-reducing measures (i.e., road improvements, emergency response improvements) to transport hazardous waste by truck and by rail. P/A-]0-4 Because planning for safe transportation oC hazardous waste is a regional concern, this jurisdiction shall work with regional transportation planners in ensuring that local issues are addressed is regional transportation plans. P/A-10-5 Because state highways are used to transport hazardous wastes through the County and it is necessary to maintain highways is good condition, this jurisdiction shall participate with regional, state,- and federal governments in determining priorities for funding and repair of highways in the County. P/A-10-6 Because transport of hazardous waste on local roads has not • been considered, this jurisdiction shall study and develop transportation and routing plans for the transport of hazardous wastes within urban areas. • P/A-10.7 Because knowledge about safe transportation of hazardous waste as well as state and federal transportation regulations is important Cor proper management of hazardous waste, this jurisdiction shall continue its education program Cor hazardous waste generators. The program shall include information on proper labeling, placarding, and manifesting requiremenu. P/A-]0-8 Because transportation of hazardous materials is an important issue that needs further consideration, and because current plans do not address the transportation oC hazardous materials and these materials are transported through the County on a regular basis, this jurisdiction shall require the task force identified in Policy P/A-]0-2 to consider transportation of hazardous materials issues as well as those of hazardous waste. 10-9 l 71 y M}. CHAPTER 10 -TRANSPORTATION 1. Anthony, Douglas K.. Project Coordinator for LPG/NGL Risk Assettment, County of Santa Barbara, Department of Resource Maaagemeat, personal communication. 2. Ayala, Lieutenant Mike, California Department of Highway Patro4 personal communication. 3. California Vehicle Code, Section 31304 and 31305. 4. California Chamber of Commerce, Hazardous Waste. Management Handbook' Guidelines for Compliance. May, 1987. 5. County of Santa Barbara, Department of Resource Management, Request for Proposal -Risk Assessment of ('.*s Liouide_ Transoortation_ May, 1988. 6. San Bernardino County General Plsn Updatc, Background Report- • Transportation/Circulation Issues July, 1988. 7. Southern ~ California Association of Governmenu, Draft Regional '" Mobility Plan. September, 1988. 8. Southern California Auociation of Governments, Southern California Hazardous Waste Management Project, Potential for Hazardous Waste Transport by Rail. January, 1985. 9. U.S. Congress, Office of Technology Assessment, Transoortation of Hazardous Materials. OTA-SET-304, July, 1986. • lo-lo • CHAPTER I1 ENFORCEMENT AND EMERGENCY RESPONSE 11.1 INTRODUCTION Enforcement and emergency response are two critical elements necessary Cor the effective management of hazardous waste and materials. The County's enforcement program ensures compliance with hazardous material/waste regulations by conducting both investigation and, possibly, litigation of potential violations. The emergency response program, on the other hand, consists of an emergency response team composed of active trained Dersonoel and a model emergency response plan (Area Plan) that identifies the resources and responsible agencies in the event oC an emergency. These programs are critical because they ensure compliance with hazardous material/waste regulations and the local jurisdiction's preparedness in the event of an accidental spill or release. Also, important to proper management of hazardous material/waste are inspection and monitoring efforts. These issues are discussed in Chapters 6 and 7. 11.2 ENFORCEMENT The County Department of Environmental Health Services (DEHS) responds • to complaints regarding management of hazardous material and hazardous waste in the County.. Complaints are received both from the public (via a toll-free number) and from the State Department of Health Services (DHS). Complaints received from the State are primarily notifications of discrepancies on manifest forms. DEHS inspectors respond to complaints by verifying the type and severity of the infraction; by ensuring appropriate measures are implemented to clean up or properly address the violation; and by providing regulatory information so that the violator knows and understands the requirements. Inspectors may issue a Notice oC Violation (NOV) to correct a serious or recurring violation. The NOV specifies the type oC violation, the manner in which the violation must be corrected, and the time period for compliance with the regulations. The DEHS inspectors monitor compliance with the NOV. In the case of serious violations which may pose imminent danger to public health and safety, enforcement is coordinated through a multi- agency team called the Strike Force. The DEHS coordinates the Strike Force which includes representatives Crom the County Sheriffs Department and [he District Attorney's office and the California Highway Patrol. The Strike Force combines the expertise of the law enforcement agencies with that oC the environmental health agency. It meets regularly to coordinate the investigations of major hazardous waste violations and to evaluate the severity of a violation and determine the appropriate course of action. The Strike Force gathers evidence for those cases anticipated to go to court. • The DEHS allocates thirty-six budgeted positions to work directly on hazardous material and hazardous waste inspection and enforcement 11-1 n LJ eCforu. Many of the professional staff have worked in the haurdous % material/waste field for four to seven years. Given the newness of the field, the length of DEHS experience in haurdous material and waste management is significant. The DEHS professional staff also have solid educational backgrounds with advanced degrees in the following arcs: public health, environmental health, biology, chemistry, geology, and other related sciences. The DEHS has developed a training program for new employees. Also, the DEHS supporu and encourages all employees to ake outside training courses offered by higher education programs, and to attend workshops, conferences, and seminars. The inspection and enforcement eCforu are supported by permit Cees. If a specified haurdous waste facility were developed in the County, additional staff would be necessary to provide inspection, monitoring, and enforcement efforts Cor the facility. Funding for such positions could come Crom the ]096 tax provided Cor under state law. It is difficult, however, to assess how many positions would be necessary since the exact number would depend on the size and type oC facility proposed sad whether a Contract or permanent position would be necessary. The latter requires further investigation on the County's part to evaluate the advantages and disadvantages of either type of employment scenario. 11.3 EMERGENCY RESPONSE Fcderal, state, and local agencies play a role in emergency response • eCforu. The federal government takes an advisory and coordinating role, except with regard to iaeidents where a substantial thrut exisu or where ~;' the state and local agencies do not have the resources to handle the situation. The sate provides information, funding, and assistance. The local agency provides a more comprehensive response to an emergency because of available local expertise and the local agency's preparedness in response to an incident. 113.1 Federal The Comprehensive Eavironmeatal Response, Compensation, sad Liability Act (1980) authorizes the federal government to assist state and local governmenu in providing t comprehensive response to accideaul releases oC haurdous materials. Response to an emergency is handled either by the EPA for areas on lead or the Coast Guard for accidental releases in or near coastal waters. Federal law requires the releaser to notify local agencies of the release as welt as the National Response Center in Washington. If a relcasc is very serious or beyond the capability of the local jurisdiction, the National Response Team may be called is to assist with clean-up. 1132 Stau The State Superfund (or Carpenter-Presley-Tanner Haurdous Substance Aeeouat, 1981) alloutes state funding to assist in responding to a • haurdous materials release. The funds may be used by state and local 11-2 ~ • • agencies to purchase emergency response equipment; limited funds are available for clean-up actions. The California State Hazardous Material Incident Contingency Plan identifies the responsibilities of the state agenciu in responding to an emergency. The state response to as incident is coordinated by the State Agency Coordinator (SAC). The SAC must coordinate the on-scene operations of all state agencies. When releases occur on state freeways, the California Highway Patrol is the SAC. For off-highway incideau, the Department of Fish and Game is the SAC. 11.3.3 Local The County oC San Bernardino has had an emergency response program in place since 1981. This initial program consisted oC a model Hazardous Materials Emergency Response P-an (HMERP) used by local and state agencies to develop similar plans. A DEHS agency response team was also part of the initial program, however, a small number of budgeted positions existed at that time. The team grew from one half-time position to three full-time positions. Because the initial response team was small, it was difficult to have trained staff in all areas of the County. Therefore, in 1984 the team was expanded to allow Cor the participation oC local cities and County Fire district personnel; this .provided for trained staff in different geographical areas of the County. The Plan was also revised • at this time. The San Bernardino County Interagency Response Team is still active and consists of representatives Crom the Cire service, law enforcement, and related public service agencies Crom the cities and the County. The team trains together about once or twice a month. The HMERP has been revised again to address requirements under state law. The Area Plan (supercedes HMERP) authorized under AB 2185 (Chapter 1167, Statutes of 1986) was prepared as a joint effort of the Cire service, law enforcement, public service agencies, and private industry. The development oC the Plan was coordinated by the County Department of Environmental Health Services. The Plan defines a course oC action in the event of as emergency and provides information on safety requirements that 'can be used in training personnel. More specifically, the Plan identifies responsible agencies and their organizational roles, procedures for responding to an incident, evacuation procedures, hazardous chemical information sources, and spill countermeasure resources. The Area Plaa identities the following agencies as those agencies involved in an emergency situation; they include: Law Enforcement -Scene manager for on-highway incidents. For off-highway incidents the law enforcement agency would only assume such a role in the absence of the fire authority. Ensures security oC the site, provides crowd snd traffic control, takes all feasible steps to protect life, prevents handling of hazardous materials, and notifies other agencies as required. • 11-3 • s ~~ Fire Service -Scene manager for off-highway incidenu and in the absence of law enforcement would also assume such a role for on- highway incideau. Ensures public safety, coordinates medical operation unfit relieved by the public health officer, takes all feasible steps to protect life, and preveau handling of hazardous materials. F_mer¢encv Services Bureau/Sheriffs Office - Cootdiaatu with responding agencies and evaluates severity of the situation. Notifies appropriate governmental bodies if the incident is serious. Identifies unknown hazardous materials and provides information on the proper handling and disposal of the materials. Initiates legal action against parties responsible for spill or release. Environmental Health Services Department - Assists in identifying spilled materials, provides on-the-scene and/or telephone information on potential health hazards of identified haurdous materials. Furnishes information on proper handling cad disposal of hazardous materials. Provides enforcement and initiation of legal action against parties responsible for spill release or illicit disposal, and violations of hazardous materials transportation and handling regulations. Public Health Department - Provides and coordinates emergency medical resources Cor spills involving say human exposure. Public Information Officer - Answers questions from the media ,, regarding the incident. - The Area Plan also identifies ancillary agencies that would be called upon for special circumstances. These agencies include the Regional Water Quality Control Board, the District Attorney, the County Department of Transportation, the State Department of Health Services, Cal Trans, the State Office of Emergency Services, the US. Forest Service, the Bureau of Land Management, and the US. Coast Guard. A regional emergency response plan has also been prepared as authorized by the Superfund Amendment and Reauthorization Act (1986). The Local Emergency Planning Committee prepared the regional emergency response plan. The purpose of the regional plan is to coordinate regional assistance for those incidents which go beyond the capability of the ioeal area. Information from County Area Plana have been incorporated in the Plaa. The Plan was developed for Region VI which includes Mono County, Inyo County, Saa Bernardino County, Riverside County, Imperial County, and San Diego County. 11.4 GOALS AND POLICIES/ACTIONS 11.4.1 Goals G-11-I To ensure the safe management of haurdous substances within San Bernardino County. ••.. 11-4 'G-II-2 To continue providing a comprehensive response to emergency situations in order to protect public health and safety and the environment. I1.4Z Policies/Actions P/A-ll-1 Because consistent, periodic inspections of hazardous route generators in thb'County ensures compliance with hazardous material/waste regulations, the County shall continue to conduct a hazardous waste generator sad haurdous material handler inspection program. The program shall emphasize education sad technical assistance to hazardous material handlers and hazardous waste generators regarding regulatory requiremenu sad route minimization. Every effort shall be made to implement this program in all areas of the County. P/A-11-2 Beesuse inspection and enforcement efforts are conducted by several different agencies and a combined enforcement program may ensure continued compliance by businesses in the County, the County shall continue to coordinate enforcement efforu with the State Department of Health Services, the Regional Water Quality Control Boards, the Air Quality Management Districts, and other federal, state, and local agencies. • P/A-I1-3 Because enforcement efforu provide a mechanism Cor ensuring compliance with haurdous material/waste regulations, the County shall continue to fund the enforcement program through permit fees. P/A-11-4 Because emergency response procedures involve several different agencies, the County shall develop an on-going awsreneu program that informs the police, fire, and other agencies about the procedures and responsibilities specified in the Hazardous Materials Response Area Plan. P/A-11-5 Because the County has significant expertise in coordinating responses to emergencies, the County shall continue to be the coordinating agency for the Interagency Response Team. P/A-1]-6 Because response to an emergency requires trained, experienced personnel, the Interagency Response Team shall continue its advanced response capability training. • 11-5 CHAPTER 12 SITE MITIGATION AND LONG TERM REMEDIAL ACTION 121 INTRODUCTION The prevalence oC hazardous materials and produce has been widuprgd throughout the County and cities, as thue produce are commonly used in our society. The consumer demand for these materials requires that businesses handling hazardous materials and generating hazardous waste be located in every jurisdiction. Such materials and wastes have been produced and handled for many years, sad accidental releases oC theu materials have created a multitude of contaminated sites. The most common threat associated with these sites is the potential movement of hazardous contaminants through the land to water supplies, particularly groundwater aquifers. Other problems associated with contaminated sites include: toxic emissions, improper land use in areas on or surrounding contaminated sites, and short or long term risk to public health and safety. Several federal, state, and local programs have been developed to identify, charac[erize, and ultimately mitigate contamination and potential negative impacu at these sites. These programs have resulted in several lists which identify sites targeted by each program. Theo lisu often duplicate • each other, although considerable difference occur among the lists. While data are being compiled on theu sites, they are incomplete becauu there are difficulties in tracing boundaries of operation, Cindiag responsible parties, sad fatly suessing the extent of the potential contamination. The available data are maintained by many separate agencies, and risk determinations and mitigation methodologies arc not yet completed for most oC these sites. In addition, these lists may change as sites are discovered, created, or mitigated. This chapter briefly reviews some of these programs and their resultant site lists. The objectives arc to ensure that jurisdictions are aware of these sites, that timely and complete cleanup occurs, and that proper impact review is conducted as a part of the development/land use review process. When data on hazardous waste generation projected from cleanup efforts are made available by the responsible agency, it will be included in the data analysis section in future revisions of this Plan. However, most sites have not yet been evaluated by the responsible agency. 122 IDENTIFICATION OF SITES There are a number oC different fists which identify contaminated sites targeted for cleanup, including the following: Bond Expenditure Plaa Sites Leaking Underground Storage Tanks Toxic Pits Subject to Closure `,_ • Identified Hazardous Waste Sites 12-1 12.2.1 Bond Ezpenditure Plan Sites The cleanup oC contaminated and abandoned sites is authorized under the Federal Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA or Superfund) and the Carpenter-Presley- Tanner Hazardous Substance Account Aet of 1981, referred to u the State Superfund. Both Acu provide the authority and funding neeesury for federal and state governmenu to respond directly to any problems at abandoned and contaminated haurdous waste sites, not only in emergency situations, but also at sites where the contamination has been present for some time. ' The Expenditure Plan for the Hazardous Substances Cleanup Bond Aet lists the principal contaminated sites in the state. These include federal Superfund sites, situ to be cleaned up by the state, and sites to be cleaned up by private parties. Bond Expenditure Plan Sites within Sta Bernardino County are identified in Table 12-1. The Site Specific Workplans for the Abatement of Listed Sites as published by the Department of Health Services Toxic Substances Control Division, January, 1988 are presented in Appendix G. 12.2.2 Leaking Underground Storage Tanks The Department of Environmental Health Services (DEHS) maintains a list of sites at which cleanup is being carried out following removal oC a leaking underground storage tank. For those instances where the leaking tank threatens contamination of the groundwater, the respective Regional Water Quality Control Board (RWQCB) is responsible for overseeing the cleanup. Where only soil contamination is involved, DEHS oversees the cleanup. This list is updated periodically to reflect the current states at each site. (Note: Each regioasl board also mainains Iisu of LUST'S.) I]_2.3 Tozie Pits Subject to Closure The Toxic Piu Cleanup Act of 1984 restricu the use of pits, ponds, wad lagoons for the disposal of hazardous waste. This law requires that existing facilities which pollute or threaten to pollute the waters oC the state either retrofit to meet new standards or close the impoundment The Regional Water Quality Control Boards are responsible for overseeing site cleanup during closure. Table 12-2 ineludu a list oC toxic pits in San Bernardino County. 1224 Office of Planning and Resurch Compilation of Identified Hazardons Waste Sites California Government Code requires the Office of Planning and Research to compile and provide to local jurisdictions a list of conaminated sites within that jurisdiction. Although this list is compiled from several sources, timely submission of updates, additions, wad deletions to this list is difficult to achieve on a statewide b:sis. Since this list is intended for daily usage during the development review and permitting process, • ~. • _. '; 12-2 TABLE 12-1 EXPENDITURE PLAN SITES IN SAN BERNARDINO COUNTY' • • :._ AIR FORCE PLANT 42 BARSTOW/MARINE CORPS LOGISTICS BASE CRAFTON-REDLANDSAREA DAGGETT AIRPORT FORT IRWIN NATIONAL TRAINING CENTER GENERAL ELECTRIC ENGINE MTC, CENTER GEORGE AIR FORCE BASE ISAAC COHEN AND SON, INC. KAISER STEEL SITE KOPPERS -ONTARIO MOJAVE NAVEL WEAPON CENTER-RANGE B NORTH SAN BERNARDINO AREA NORTON AIR FORCE BASE R'ESTERN STATES REFINING YERMO TRUCK STOP/GROUND WATER Palmdale Barstow Redlands Vicinity Daggett Fort Irwin Ontario V ictorville Ontario Fontana Ontario China Lake North San Bernardino San Bernardino Fontana Yermo 'Source: 'Expenditure Plan for the Hazardous Substance Cleanup Bond Act of 1984, Revised January, 1988' prepared by the California Health and Welfare Agency, Department of Health Services, Toxic Substances Control Division. 12-3 • 'r TABLE 12-2 TOXIC PITS IN SAN BERNARDWO COUNTY (Identif ied as of Deeember~ 19gg) ~= SIICc No. of Pita Aeroehem El Mirage 1 AT & SF Railway Barstow 2 Kaiser Steel (Chemwest [nd.) Fontana $ Kerr-McGee Searles Lake 1 Molycorp,Ine. Ivanpah Ponds 2 Molycorp, Inc. Surge Poads 1 Norton AFB San Bernardino 1 Pacific Gas & Electric Topock Compressor 4 Southern California Edison Etiwanda Generating Stn. I Southern Pacific West Colton Yard ! U.S. Marine Corps Twentynine Palms 1 SOUrCG: California Department of Health Services Memo, 'Other Data Sources and Site Mitigation Waste'. Supplemented by telephone calls to the three Regional Water Quality Control Boards. 12-4 • effort should be made by agencies, the local jurisdiction, and DEHS to review and update this list on a frequent and periodic basis. 12.3 OVERSIGHT AT CLEANUP 12.3.1 Coordination Many sites are subject to the review and jurisdiction of more than one agency. As discussed previously in this chapter, there is a joint responsibility between the RWQCB and DEHS ss regards the cleanup of leaking underground storage tanks, depending on whether or not groundwater is threatened. As work proceeds on closure oC Toxic Pits, there is a need for DEHS to work with the RWQCB in order to develop planning estimates of the waste which will be removed from the sites. Similarly, DEHS needs to work closely with the State DHS, the ]cad agency for cleaaup of Expenditure Plan Sites. For some sites on the list, it may be appropriate and efficient for DEHS to provide day to day oversight oC sampling and remediation activities. CERCLA and the state superfund provide that DEHS, local jurisdictions, and the Dublie may review determinations made during this site assessment and cleanup process and par[icipate in the process. DEHS needs to work closely with the State DHS in order to develop planning estimates of the wastes which - will be removed From the site. • I2.3.2 Locsl Responsibility DEHS has responsibility to insure that the responsible party provides cleanup oC the contaminated sites located in the County. These include: (caking underground storage tank sites, certain iadustrial releases, and releases due to illicit dumpings, transportation accidents, and other findings during Haz-Mat Team/Strike Force activities. San Bernardino County should develop a site mitigation program to be administered by DEHS which would be responsible Cor the monitoring of cleanup at such sites throughout the County. Such a program would include: a) Identification/Initial Investigation, b) Emergency Aetioas to Eliminate Acute Threat to Public, c) Public Notification, d) Responsible Party Identification, e) Site Assessment and Characterization, f) Remedial Action Proposal, g) Remediation, h) Finalization, and i) Cost Recovery. The objective oC this program is to identify contaminated sites, and to find a permanent remedy that is technologically feasible and reliable that effectively reduces the danger of contamination, and that adequately • protects public health, welfare, and the environment 12-5 In addition, this program could act as a local reviewer and advocate to insure, regardless oC the responsible agency, the appropriate remedial responses are taken to insure a permanent remedy for all sites 12.4 DEVELOPMENT/LAND USE APPLICATIONS AT LISTED SITES California Government Code, Seetioa 65962.5 requires that an applicant for any development project consult the Office of Planning and Research (OPR) list oC contaminated sites and submit a signed statement indicating whether the project is located on a site which appears on the OPR list The state law does not indicate what action a local jurisdiction must take in the event s development proposal is Iocatcd on a listed site. In order to insure appropriate and uniform review of projects, the following requiremenu should be considered: - a) the local jurisdiction, DEHS, the agency which listed the site, and the applicant should confer prior to determining an application complete. The purpose of the meeting shall be to identify appropriate review requiremenu necessary for the local land use or building permit application process. b) All app[ieations proposed on a listed site should be subject to local jurisdiction discretionary site review/conditional land use review processes, unless it is determined by the local jurisdiction that such discretionary review is not necessary. This procedure will insure projecu proposed on contaminated sites receive appropriate local review. I23 COORDINATION OF' ASSESSMENT AND CLEANUP AT SOLID WASTE SITES The DEHS is the designated Local Enforcement Agency for oversight of operations at solid waste landfills. As a result of a number of new monitoring programs being instituted, several solid waste landfills are identified as contaminated sites. Because several agencies have jurisdiction over some aspect of cleanup, and because many of these sites are owned by governmental entities, a coordination of effort, both for assessment and cleanup at these sites is accessary. It is recommended that the County convene a Task Force of affected agencies for each specific site to coordinate efforu. I2.6 GOALS AND POLICIES/ACTIONS The following goals and policies/actions address the need to coordinate activities related to site mitigation sad long term remedial action. 12.6.1 Goals G-12.1 To ensure that all jurisdictions are aware of all identified contaminated sites within San Bernardino County. • • 12-6 ~' • G-12-2 To ensure that timely and complete cleanup occurs at contaminated sites. G-12-3 To ensure that environmental review is conducted Cor projeeu proposed on sites which have been identified as contaminated. 12.6.2 Policies/Actions P/A-12-1 Because current information on the location and status of cleanup oC contaminated sites is of vital importance for development in the County, and because the Office of Planning and Research (OPR) List is not frequently updated nor don it provide details as to the contamination or status of cleanup, this jurisdiction shall develop a contaminated sites data base that provides geographical, physical, and land use characteristics for use by applicants and industry. In addition, the County Department of Environmental Health Services (DEHS) shall update the OPR list on a periodic basis and provide a DEHS updated list to each jurisdiction. -The DEHS updated list shall also be used by this jurisdiction to assist in identifying contaminated sites associated with land use applications. During DEHS preparation of an updated list, the following may be included: • a) information on site contamination and its applicability to different types of development to assist cities and applicanu, b) information regarding the current cleanup status of contaminated sites, and c) addition of sites to the OPR list. When DEHS proposes to add a site to the OPR list, DEHS shall first notify the owner in writing. Analytical evidence shall be required before s site is listed. The owner shall have 15 days from the date of this notice to make a written request for a Administrative Hearing regarding the proposed listing. When requested, a hearing shall be held prior to listing a site as contaminated. P/A-12-2 Because cleanup of contaminated sites is a complex task which involves multiple agencies, DEHS shall monitor and work cooperatively with all agencies involved in site assessment and remediation. DEHS shall consider developing a Memorandum of Understanding with state and regional agencies to provide assistance and oversight of monitoring, assessment and/or remediation activities. P/A-12-3 Because the method of remediation can cause impacts, the County and cities in conjunction with the State Department of Health Services shall encourage onsite treatment and remediation • to reduce the transport of hazardous waste from contaminated I2-7 sites, and should insure appropriate remediations are completed to provide permanent remedies. P/A-12-4 Because site remediation activities require coordination sad expertise, DENS shall implement a site assessment sad remediation program and develop a program to enhance training of personnel is site assessment and mitigation techniques, and risk assessment techniques. P/A-12-5 Because site assessment and remediation creates cosu to the local agencies, the County should investigate Cuadiag possibilities for cleanup activities. This should consider how local agencies can recover full or partial payment from responsible parties for cleanup of contaminated sites, reduce the duplication of effort among all agencies, cad minimize the cost of work. The County sad cities should support legislation that defines the responsible party in regard to the assessment and cleanup of contaminated sites, as well as legislation that improves access to state and federal Superfunds to cleanup orphan sites. DENS should seek state funding for underground storage tank remediation programs. P/A-12-6 Because state law does not specify local actions or procedures for projects proposed at a location listed by the Office of • Planning and Research (OPR) as a contaminated site, and impacts may result to the public health and safety, and because development on contaminated sites may preclude future environmental remediation this jurisdiction shall amend the Development Code to implement the following as a part of the development review and permit issuance process: e) require a preapplication meeting for all development/land use applications at locations listed by OPR or DEHS. b) require all development/land use aDDliestioas at locations listed by OPR or DEHS to be subject to discretionary conditional use review of this jurisdiction, except when deemed not necessary by this jurisdiction. Exemption from discretionary review shalt be based on the scope oC the project and the nature of the contamination. P/A-12-7 Because this jurisdiction has a concern with proper cleanup and funding for cleanup of contaminated sites, this jurisdiction shall do the following: s) Recommend, by resolution, to federal legislative representatives that legislation be developed to require Department of Defense to include site cleanup and to set. aside money for cleanup (at present cost) as part of base closure plans, and 12-8 • • b) Require that a clean-up plan which funding be submitted to DEIiS for before new or alternative land uses a includes the source of rcview and approval re undertaken. 12-9 • CHAPTER 13 PUBLIC EDUCATION AND PARTICIPATION 13.1 INTRODUCTION An effective public participation program depends on early and continued planning to generate input from a broad Dross section of the population and the regulated community. The overall public participation program for the CHWMP allowed Cor public input on concerns and priorities; suggestions for alternatives and new strategics; and review and attessment of proposed measures. An effort was made to inform and encourage participation Crom the general public, civic, environmental and business organizations, the cities and agencies within the County, and the regulated community. Also, the services of a public participation coordinator were secured to assist department staff in implementing a public involvement program. An extra effort was made to get input by early November to meet the December 31, 1987, Draft Plan deadline. Preparation oC the final CHWMP required additional public involvement efforts. The CHWMP public participation program consisted of the following elements: - on-going advisory committee input • distribution of newsletters distribution of an informative brochure - a series of public workshops - a speakers bureau and slide presentation - media coverage - distribution of 3000 copies oC the draft plan summary and about _ 750 copies of the Draft CHWMP - a series of public hearings on the Draft CHWMP 13.2 PROGRAM COMPONENTS 13.2.1 Advisory Committee The CHWMP Advisory Committee consisted oC ]0 members. The Advisory Committee included one environmental representative, two industry representatives, Cour public represcntatives, and three City representatives. A list of the Committee members and their backgrounds is presented in ADDendiz H. The Advisory Committee has two major functions identified in state law. The first is to advise decision-makers on issues related to the development, review, and approval oC the Plan, as well ss on issues related to the overall development, content, and future administration oC the Plan. The second is to hold informal meetings and workshops to inform the public and to receive commenu on the CHWMP. • The Committee met regularly throughout the preparation oC the CHWMP. All Committee meetings were open to the public. At these meetings the 13-1 _ -. r1 ~.I Committee dealt with and decided on major issues associated with the preparation and adoption of the CHWMP. Some oC these issues included the public participation Drognm, the siting criteria, the data, waste - minimization, hazardous materials management, and the goals and policies for long-term management of hazardous wastes. The Committee significantly revised the Draft CHWMP based on commenu received from the public, the State Department of Health Services, and federal, state regional, and local agencies: The Committec Geld public workshops and hearings to reeeivc input oa the Draft CHWMP ss required by the Tanner Aet. The County Board of Supervisors delegated the authority of conducting these hearings to the CHWMP Advisory Committee. The workshops were held prior to the preparation of the Draft CHWMP to obuin input on the issues to be addressed in the Draft (see following discussion 13.2.3). UDOa completion of the Draft Plan, Dublic hearings were conducted to receive comments on the Draft. Department staff presented the Draft Plan to City deeisioa- makers at noticed public hearings. These presentations were made between 3anuary through March of 1988 before the City Council or Planning Commission (or both) of each of the cities (see Appendix H). The cities were presented with a discussion of the major issues presented in the Draft CHWMP. Commenu from the cities were taken and their continued involvement in the preparation and adoption of the CHWMP was encouraged. Hearings, separate from the one before decision-makers, were Geld to encourage public input on the Draft CHWMP. 13.2.2 Newsletters A brief newsletter (Update) was published periodically during the early preparation of the CHWMP. The newsletter provided background information on hazardous waste management issues and options regarding the siting _ criteria, a summary of Advisory Committee meetings, and a achcdule of meeting dates. The newsletter was distributed to several organizations sad individuals These organizations are shown on Table 13-1. 1323 Public Workshops Siz public workshops were held throughout the County. The purpose of these workshops was to solicit input on the issues to be addressed in the CHWMP and the Environmental Impact Report. Since the workshops were well attended, substantial public comment was received. The comments focused on issues regarding the siting of specified haurdous waste facilities, waste management wad reduction, the definition of 'fair share', educational programs, and much more. Generally. there wan sa ovenli concern for how the County would view the siting process Cor the different hazardous waste management facilities. See Appendix H for a achcdule of these workshops wad a listing of the commenu received at the meetings ~: 13-2 ~:. .. :_ TABLE 13-1 UPDATE MAILING LIST Advisory Committee Chambers oC Commerce Cities: Mayors, Council Members, City Directors Organizations: Sierra Club Audubon League of Women Voters Automotive Service Council Desert Planning Hi Desert Citizens Against Pollution Yucca Loma Homeowner's Association Building Industry Association Private industry Council Government Agencies: Water Districts Water Boards Air Quality Districts • 1324 Brochure i Managers, Planning ]n addition to the newsletter, a brochure was developed. The brochure provided background information on the purpose and need for the CHWMP. It provided a brief summary of the definition oC hazardous waste and the dangers associated with improper management. The brochure was distributed at public meetings and throughout the County. The brochure o a description oC the Tanner o a table identifying possible o a description of various facilities; and was available at public counters included the following information: planning process; siting criteria; types of treatment and disposal o a discussion oC waste minimization. 1325 Speakers Bureau and Siide Presentation A general information slide show was developed in cooperation with U C Riverside Extension for use at public workshops. Presentations were made to community organizations, city councils, and planning commissions, including: • Redlands Kiwanis, • San Bernardino Kiwanis, • American Association of Retired Persons, • Sierra Club, • • League of Women Voters, • Fontana Planning Commission, and • Victorville Chamber of Commerce 13-3 Victorville Optimist Club Redlands City CouaeiL 1326 Media Coverage The preparation oC the CHWMP received coverage on the radio and general circulation newspapers. Several major articles were printed in local aru newspapers announcing the dates, times, and purpose of the workshops as well as their outcome. The meeting agenda for all Advisory Committee Meetings were noticed in local newspapers. Medu coverage was augmented by the appeanna of a staff member as the featured guest on a local Spanish language radio talk show. 1327 City sad Ageary Review Group The City and Agency Review group met monthly during plan preparation to consider the Advisory Committee`s actions and to advise staff about the plan. The informal review group included representatives from the cities, the Regional Water Quality Boards, Air Districts, and the Buruu of Land Management. 132E Draft Plan Distribution Aa extensive effort was made to receive public comment on the Draft • CHWMP. In additioq to public hearings oa the Draft, the Draft CHWMP and the Draft CHWMP Summary were distributed tbrougbout the County. The Executive Summary of the Draft Plan (shoat 3000 copies), notice of all ' scheduled public hearings, sad information on locations Cor reviewing the Draft CHWMP were sent to everyone on the UPDATE mailing list. About 750 copies of the Draft CHWMP were distributed to all the cities in the County, public libraries, ail affected agencies (including County departments like the Lsad Management Department), federal, hate, and regional agencies, interested groups (such :s environmental, civic, industry), local Indian Tribes, local legislators, and water agencies. A significant number of comments were received on the Draft CHWMP as .a result of alI the public involvement efforts. The response to commenu is presented in Appendix J. 133 ON-GOING PUBLIC EDUCATION/PUBLIC PARTICIPATION Successful implementation of the CHWMP will depend oa continuing public education on the importance oC proper haurdous waste management Continued efforts is this area will aced to focus on public involvement in the implementation oC the programs specified in the CHWMP and on Dublie participation in the review of proposals Cor specified hazardoat waste facilities. 133.1 Advisory Committee The Advisory Committee provided valuable input is the preparation of the • CHWMP. Because of the diverse background of the members, each member brought a unique perspective is dealing with the different issues and 13-! ~~ ~ i problems encountered throughout the planning process. A similar Advisory Committee should be set up for the review and consideration oC the implementation programs proposed in this CHWMP. Providing for an on- going Committee would ensure public involvement throughout the development and planning of hazardous waste management programs. 13.32 Public Involvement in the Siting of Faeilitia AB 2948 (Chapter 1504, Statutes of 1986) specifies that a Local Assessment Committee (LAC) must be established upon application for a specified hazardous waste facility. The LAC must consist of at least seven members including three representatives from the community at large, two representatives oC environmental or public interest groups, and two representatives of affected businesses or industries. The LAC would: - Negotiate with the project proponent on the details oC the proposed specified hazardous waste facility; - Represent the interests oC the residents of the affected community and adjacent communities; - Receive and expend technical assistaace monies; - Adopt rules and procedures necessary to perform its function; and - Advise local decision-making bodies of the terms, provisions, and conditions oC the project which have been negotiated with the project proponent. • The LAC has an advisory role only. Applicable County or City deeision- makers may override any decision made by the Committee. Table 13-2 outlines the procedures and the scope oC work suggested in the formation of a LAC. The Regional Hazardous Wa: Participation program that applicable local jurisdiction Regional Plan points out "information" to "sharing participation must begin as phases: - Communication, • Orientation, and - Negotiation. to Management Plan describes a Model Citizen could be implemented by a LAC and the in the review of a project application. The that public participation has moved from decision-making responsibilities.' Public early as possible and should consist of three The Communication phase ensures all sides are engaged in open, credible exchange. The Orientation Phase focuses on having all interests working from the same foundation oC information. The Negotiation Phase guides the development of an acceptable solution for the siting of a specified hazardous waste facility. The Model Citizen Participation program is presented as Table 13-3. r1 U ~ ~, 13-5 TwBLE I3-r • SUGGESTED CHECKLLST FOR -- THE ESTABLISHMENT OF A LOCAL ADVLSORY CObA~ti'ITEE I. Composition: o Include seven member representing a cross-section oC the Community (see discussion on page 3-9). o No member should have a direct financial interest in the project 2. Procedure: o Establish by-laws similar to other advisory committees within uid City or County, include Brown Aet requirements. o Establish a regular schedule for meetings, i.e., dates, time, and location. o Name officers - Chair, Recording Secretary. o Identify City or County department responsible Cor staffing the committee and preparing meeting notices, agendas, and minutes 3. Scope of Work: o Develop a work program that describes Committee raponsibilities including the dutinctioa between: (1) The CEQA responsibilities of this jurisdiction's Planning • Department with the •informstion requesting' raponsibilities of the local advisory committee, (2) The multiple agency review proxss with the 'negotiating" assignment of the local advisory committee, and (3) The time schedule for the Committee's work with the State streamline permit processing requirements. o Include in the work program a discuuion of the methodology for presenting negotiated conditions to the local governing body. • This table is based on the one presented in the Draft Regional Hazardous Waste Management Plan, 1988. 13-6 ~- a r~ f`J TABLE 13-3 A MODEL CITIZEN PARTICIPATION PROGRAM • • PHASE ONE COMMUNICATION PHASE TWO ORiENTAT70N A. Identifv Citizen Inte•~~r r•ro „~ A, Information 1. List of citizen groups, leader- I. Type of Facility ship contacts,achedule oC regular meetings and newsletters 2. Pre-application Citizen Meeting o Present project idea o Establish citizen network o Identify early concerns 2. Wastes o Types of Concentrations o Sources 3. Pre-application Government Meetings o Brief elected officials o Meet with each permitting agency, seek to coordinate all permits through local government. B. Initiate Tanner Loeal Assessment Committee proeess_ Send Notice of Intent to: State Office oC Planning Assistance, County Planning Department, and Authority. C. Provide ongoing open communication. 3. Site Characteristics 4. Facility Design dt Cost 5. Permit Requirements 6. Time Horizons o Neighborhood Meetings o Public Notices o Flyers, Handouu oPre-application Meetings o Modifications to Plans 13-7 PHASE TWO PHASE THREE ORiENTATiON NEGOTIATION (Continued) B. Assessmen* A. identify the earties involy d in negotiations 1. Consistency with Regional Plan and County Plan. o Local Assessment o Siting Criteria oOfficeofPlaaningAssistaace o Needs Assessment o Authority o Permitting Agencies 2. Site specific enviroamenul o Proponent impact esessment B. Identify the issnee to be o Air o Seismic resolved o Water o Flood Plains o Soil o etc. C. Recommend the negotiat !~ 3. Facility Specific (design) solution to the local Planning Commission (City/County) assessment o Conditions of approval for o Construction -Bat the permit • Available Control Technology o Annual operating require- (BACT) - meats o Operation -Safety train- o Liability Insurance ing gad emergency response plans o Special Community Miti- gations 4. Transportation Impacts o Volumes o Routes 5. Neighborhood Compatibility 6. Public Health Riskt 7. Economic Impacts o Project vs. No-Projeet 8. Company Past Performance 9. Future Monitoring and Operation Program Source: Draft Regional Hazardous Waste Management Plan, 1988 • 13-8 '-"~ • 13.4 GOALS AND POLICIES/ACTIONS Public participation should take place throughout the implementation of the CHWMP programs as well as when applications for specified hazardous waste facilities are received. The following goals and policies/actions ensure continued efforts in involving the public. 13.4.1 Goals G-13-1 To continue public participation and public education in the implementation of the programs identified is the County Hazardous Waste Management Plan. G-13-2 To include public involvement in the review of applications for specified hazardous waste facilities 13.4.2 Policies/Actions P/A-13-1 Because public participation and education is important for the preparation and review oC the CHWMP, the County shall establish an on-going Hazardous Waste Management Advisory Committee to review reports on implementation of the plan, to consider new _ _ Drogram directions, to guide a continued public education program, and to assist in revising and updating the Hazardous • Waste Management Plan. P/A-13-2 Because state law requires the formation of a Local Assessment Committee (LAC) within 90 days after receiving an NOI, this jurisdiction shall establish by ordinance policies and procedures for the formation of the Committee, the selection oC members, and the role oC the LAC in regard to other decision-making bodies. i• 13-9 • CHAPTER 14 IMPLEMENTATION OF CHWMP PROGRAMS 14.1 INTRODUCTION The CHWMP recommends several programs which address the County's goals regarding effective hazardous waste management. In order to achieve these goals, reasonable efforts must be made to implement CHWMP programs. Implementation depends on the establishment of program priorities, the identification of funding sources, and the development oC a schedule for implementation. This chapter sets forth the framework for the process of implementation. It presents a discussion of organizational responsibilities and an implementation and revision schedule for the Plan. 14.2 ORGANLZATIONAL RESPONSIBILITIES Federal, state, and local agencies administer hazardous materials and hazardous wastes laws and regulations. The 'Guidelines Cor the Preparation of Hazardous Waste Management Plans' require that CHWMPs • address the role of these agencies in the management of harardous material/waste. The following information summarius federal, state, and local responsibilities with regard to this issue. 1421 Fedcral Responsibilities Environmental Protection Aeencv (EPAI The EPA is responsible for controlling and abating pollution in such areas as air, water, solid waste, pesticides, radiation, and haurdous materials. The EPA develops standards and regulations and can authorize state governmenu to enforce certain laws and regulations (i.e. air and water). Ia California, the EPA has given the responsibility Cor enforcing federal air quality requirements to the State Air Resources Board and water quality requirements to the State Water Resources Control Soard. In addition, the EPA works closely with the State Department of Health Services (DHS) in developing hazardous waste regulations, enforcement, and standards for land disposal. There are several laws which authorize the EPA io regulate hazardous material/waste. Under the Resource Conservation and Recovery Aet (RCRA), the EPA works with the DHS to ensure the proper management oC hazardous waste from iu generation to its disposal. The Comprehensive Environmental Response, Compensation, and Liability Aet (CERCLA) established the Federal Superfund program and provides funding for the EPA to clean up abandoned or inactive haurdous waste sites. The • Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) authorizes the EPA to regulate the use of all pesticides. Under, the Tonics Substances 14-] Control Aet (TSCA) the EPA has authority to identify and control ~ . reasonable risks Crom otherwise unregulated chemicals. While the EPA ; has little direct involvement in San Bernardino County's waste management activities, the EPA plays an important role in establishing parameter Cor state regulations Department of Transeortation (DOT) The DOT establishes and enforces regulations for thb transportation of hazardous materials sad hazardous waste. These regulations iaclnde requiremcnu for proper conninment, marking, and placarding, as well as the need for shipping papers and reporting requirements. See Chapter 10 Cor more information. 14.2.2 Stan RespoasibiIities State Department of Health Servicee_ (DHSI The DHS, the primary state agency involved in regulating hazardous waste, is responsible Cor implementing and enforcing provisions oC the State Hazardous Wastc Control Act (HWCA). DHS manages haurdous waste generation through the manifest system, the facility permitting system, and the regulation of hauling firms. Funding for remedial cleanup of hazardous waste sites, known as the state Superfund, is also administered by DHS. Air Resources Board (ARBI • The ARB is responsible for developing appropriate control methods to - . achieve air quality standards. The ARB must coordinate efforts to attain and maintain current air gna[ity standards u well as research causes and solutions to air pollntion. Two separate local divisions oC the ARB are responsible for enforcement oC air quality laws and regulations in San Bernardino County; the Air Pollution Control District is responsible fot the desert areas while the South Coast Air Quality Management District is responsible Cor the mountain and valley areas oC the County. State Water Resources Control Board tSWRC81 The SWRCB is responsible for water rights sad water pollution control The Board has primary responsibility for establishing guidelines Cor underground storage tank regulations and land disposal of haurdous wastes. The regional boards issue waste discharge permits, monimr water quality, and can take enforcement actions against violators. The County of San Bernardino fails within the jurisdiction oC three regional boards. Office of Emeraenev Services fOEC_1 The Statc OES develops and maintains state plans sad programs necessary to mitigate the effects oC natural, man-made, or war-caused emergencies OES coordinates the haurdous materials business plan and area plan provisions of AB 2185/g7/E9 (Chapter 6.95 of the Health and Safety Code). In addition, the OES has primary responsibility for administering the federal provisions of Title III of the Superfund Amendments sad Reauthoriution Aet of 1986 (SARA). although the procedures Cor addressing these requirements have not yet been established. 14-2 • California Hiahwav Patrol /CHP1 The CHP ensures the safe, convenient, and efficient transportation oC people and goods over California highways. The CHP responds to highway emergencies involving hazardous materials, inapeets and regulates commercial vehicles which carry hazardous materials, and coordinates with other agencies Cor the enforcement of hazardous waste laws and regulations as they apply to transportation. 14.2.3 Regional Authority The Southern California Hazardous Waste Management Authority (Authority) promotes, on a regional basis, programs that facilitate the siting oC facilities necessary to safely manage the hazardous waste generated by its member agencies. The Authority has served as an effective forum for discussion of the 'fair share' allocation of facilities and the establishment oC guidelines for intercounty agreements. The Regional Hazardous Waste Management Plaa, prepared by the Authority, describes regional 6aurdous generation and needs. While the Authority assists counties with siting issues, decisions on the siting oC specified hazardous waste facilities continue to rest with local governments (Refer to Appendix C for the Regional planning documents). • 14.2.4 Snn Bernardino County Responsibilities The Department oC Environmental Health Services (DEHS) is the most involved County department in the management of hazardous materials/wastes. The DEHS is responsible for monitoring industry compliance with the laws, regulations, and County ordinances regarding hazardous materials and hazardous wastes management. Since the DEHS is charged with carrying out hazardous waste/material programs throughout the County, the DEHS will play a significant role in the implementation programs recommended is this Plan. Several other departments and agencies are also involved. These other agencies include the Land Management Department, Solid Waste Management Department, Public Health Department, the Sheriffs Office, and the District Attorney's office. For more information on the role of these different County departments and agencies refer to Chapter 2. 14.25 City In"volvement The cities are required by state law to adopt some Corm oC a hazardous waste management plan within 6 months from the atate DHS approval of the final CHWMP. The law specifies that cities are required to do one of the following: • 1. Adopt a City Hazardous Waste Management Plan which is consistent with the CHWMP; 14-3 z. 3. Incorporate applicable portions of the CHWMP into the city's General Plan; or Enact an ordinance which requires that all applicable soning, subdivision, conditional use permit, and variance decisions to be consistent with the applicable portions oC the CHWWIP. Statc law does not limit the city's authority to attach conditions to the issuance of a land use application or to esablia6 requirements or siting criteria different from those identified in the CHA'hSP (SB 477, Chapter 1167, Statutes of 1987). Any such conditions or criteria establi:hed by a city must be substantiated as necessary to protect the public health and safety since conditions or criteria may be appealable to the State Appeal Board. Several programs identified in the CHwMP will necessitate the participation of the cities. City participation may range Crom adopting caning ordinance amendments consistent with CHWMP polieiu to city involvement in the seoping of studies. The suggested areas for city input are noted in Table 14-2 under responsible agencies. 143 THE IMPL.Eh~NTATION OF POLICCES/ACTIONS The programs recommended is this Plaa acre separated into three categories Cor implemcntatioa: immediate, first year, and second year implemeatatioa. The categories represent both the priority for implemeatatioa and the proposed implemeatatioa schedule. The programs placed in the immediate category (see table 14-1) reflect those programs that provide the needed fonadatioa for futnre County programs; they are the highest priority programs. Programs placed in the first and second year implemeatatioa category are also important but can be delayed because of concerns with funding or because issues .related to these programs have bees addressed by programs identified in the immediate category. The priorities may change, however, based on the availability of funding, changes in local attitudes, and the recognition of new conditions. Some programs like the ordinance amendments may be implemented all at once if staff and funding sources exist. Table 14-1 places each of the recommended programs into the following three categories: Immediate Implementation - This designation has been assigned to programs that should be implemented right away; these are the highest priority programs. These programs are critical eomponenu to the County's efforts and should be implemented without waiting for the completion of the formal adoption procett Cor the CHWMP. First Year Implementation These programs should be initiated within one year from the adoption of the CHWtvlp. Some of the programs identified in this category may be initiated sooner if funding sources are available. • • 14-4 • Second Year Implementation -These programs should be initiated within two years Crom the adoption of the CHWMP. Some of the programs identified in this category will require substantial coordination with other local and regional agencies. Aspecu of the programs in this category may have been addressed through the implementation of the programs in previous categories. The CHMv~ identifies new and expanded programs with varying degrees oC resource requirements. Ia order to maximize County resources, the programs were prioritized based on the type of program, the availability of staff and funding, as well as whether it was identified as a critical issue in the Plaa. In addition to setting priorities, potential funding sources and the responsible agencies have been identified. Several new programs are proposed in the CHWMP, these include the automated waste tracking system, the expansion of the waste minimization program, the groundwater protection strategy, the development oC programs Cor household hazardous waste management, the studies on the transport of wastes through the County, and programs that address contaminated sites. These programs are likely to require the allocation oC additional staff time and resources since they are not fully part of the County's efforts in hazardous waste management. These programs have been dispersed among the three categories in order to ensure resources are • available for their. implementation. Several major programs are included in the highest priority category because they are important to the overall efforts of the County in hazardous wastc management and because somc programs have been allocated staff and funding. The other programs or tasks identified in the Plan may be able to use existing staff since some of these programs are one-time efforts. The requirements Cor transportation studies were placed in the second year category because funding has not been identified. A study of transportation issues will be developed, however, as a result of any application Cor a specified hazardous waste facility (see chapter 10). This aDPlicant funded study is expected to be timely and should address some of the County's concerns with transportation associated with such facilities. Table 14-2 summarizes the information regarding implementation of the recommended programs. The implementation schedule, responsible agencies, resource needs, and potential funding sources have all been identified. The majority oC the programs will be funded by permit Cees. Some of the programs are one-time (i.e., ordinance amendments) efforts that can be absorbed into on-going County projects, othert like the transportation studies require the identification oC funding sources. The table preseau the County's best estimate of potential funding sources. 1422 Updating and Revising The CHR'MP • Implementation programs should be reviewed annually to consider the availability oC funds snd resources. In addition, new conditions and local attitudes may require that some priorities be modified to reflect these 14-5 r1 LI concerns. The Government Code (section 65400) specifies that an annual report on the implementation of the recommended programs in the i General Plan be prepared. Siaee the CHWMP is an element of the General Plaa such a report should be developed on the programs identified in this Plan. Asidc Crom reviewing the implementation programs, the entire Plan should be revised on a periodic basis to address changes in local attitudes, to update the data on hazardoua waste generators, and to verify the implementation status of certain programs. The DHS suggcsu that the CHWMP be revised on the ume schedule as the mandated revision to the State Plan. This will ensure that state and local plans are maintained on similar schedules. Table 14-3 presents a modified version of the schedule recommended by the DHS. Suggested data for subsequent revisions to the CHWMP have been included on this table. The time frames suggested is the DHS Guidelines have been adjusted to reflect legislative changes. 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C Y ~ •.~i 6 i1•• • w•O C=Y !. ~+9• ^ C++4N M d M•C Y• • •^•i0 tiPw •> M •N• ^L>M 7 O Oyy~O G~•Y • • Y • • d• O O • Y.1 P•rlr 8...> r Y ~ ~ O O ~ ~ b/ r • OC L Ci CS ~ Y • •MO Y OY i.• Ot • M > .r~ V j'.VY Yi7~ • eYO o YYY 3 a ' ^ ~ u ' 00 ~ ' ~ ~ .. y , g 1 L 1 M M 1 0 ~ O I O M p L~ M ^ .••9~~ • w W •p X 0 ( 1 p p p y C) ~ L i n Q q ~ /~ M Y • ..~ O '•' ••I 6• 10 f • TABLE 14-3 PROPOSED SCHEDULE FOR UPDATING THE HWMPi SUGGESTED SUGGESTED CURRENT FIRST SECOND HWT~[P = REViS1ONs REVISION Guidelines issued by DOHS 6/30/87 12/31/92 12/31/95 Draft Pian due to DOHS 3/31/88 9/30/92 9/30/96 Draft Plan approved by DOHS 6/30/88 12/31/92 12/31/96 Final Plaa due to DOHS 6/01/89 9/30/93 9/30/97 Final Plan approved by DOHS 11/30/89 12/31/93 12/31/98 Final State Plan issued ~ 11/30/95 11/30/98 • t The time frames presented in the table are based on. figures printed is California Department of Health Services, Toxic Substances Control Division, Guidelines for Prenaratien of Hazardous Wastc Manaeement Plans. 1987 = These are the deadlines as they have been modified by legislation that passed after release of the guidelines. 3 Because of legislative changes to the deadlines for the current HWMP, the time frames published in the guidelines are no longcr applicable. The suggested schedule for revisions to the Plan presented in the Guidelines have been modified by the addition of three years to reflect these changes. 4 The Guidelines suggest a 12/30/89 date for the completion oC the final State Plan. Given all the legislative changes, this suggested date is no longer practical. 14-15 e A) B) C) D) E) F) G) H) I) 1) e , h e . . APPENDICES DeriDitiollJ SUllllllary or LeSislatiOD ArrcctiDI Hazardous Wute aDd Material RegioDaJ Fair Share PriDciplc:a alld Authority All'CClllCJlt Wute Codes, Wute Groups, alld Gelleralized Treatmeat Methods 111StirieatioD Cor the SaD BerDardillo COUDty SitiDg Criteria Gelleral DesigllatioD Maps State ExpeDditllre PlaD Public EdueatioD alld ParticipatiOD Hazardous MateriaJs/Wutc:a Directory Commellts Received OD the DraCt CHWMP alld Rc:apollK to CommeDts (A separate dOCllmeat) . . e APPENDIX A. GLOSSARY e e . . e APPENDIX A GLOSSARY Active Fault. a fault along which surface displacement has occurred during Holocene time and .is associated with one or more of the fOllowing: a recorded earthquake with surface rupture, fault creep slippace, and/or displaced su,vey lines. Acute: an effect which is manifested soon after exposure to a hazardous material. Acutelv Hazardous Materials' any chemical of the list prepared by the Environmental Protection Acency and classified as an acutely toxic material according to the criteria set forth in the Chemical E.mercency Preparedness Program Interim Guidance document on November I, 1985, and any supplemental amendments to the document. The list is published in 40 CFR part 355. Acutelv Hazardous Waste: a hazardous waste which includes any acutely hazardous material (see above) as a constituent. e Aoueous: of, or relating to. or resembling water. Aoueous Treatment. treatment of water contaminated with hazardous materials. Consists of removing heavy metals. neutralizing acid or basic solutions, removing organic chemicals, and otherwise reducinc levels of contamination in water sufficiently to allow the treated water to be discharced into sewers or other water ways in accordance with discharce permit requirements. Residual sludges require disposal, after stabilization. , Aouifer: a ceologic formation. croup of formations or part of a formation capable of yielding a significant amount of cround water to wells or springs. (CCR. Title 22. Section 66011.1) Aouifer Rechar2e Areas' a land area where water, from precipitation. infiltration from surface streams or impoundment areas or other sources. soaks into the ground and enters an aquifer. Area Plan: the county.wide plan for response to emercencies involving hazardous materials or hazardous wastes. . . Buffer Zone: an area of land which surrounds a hazardous waste facility and on which certain land uses and activities arc restricted to protect the public health and safety and the environment from existing or potential hazards caused by the miCrltion of hazardous waste. (California Health and Safety Code Section 25110.3) e Business Pia n: a platt which includes an inventory of hazardous materials onsite; an emercency response plan. and procedures in the event of a A.I . . e release that includes notification, mitilation, and evacuation measures, and employee traininl procedureL Each Cacility site or branch oC a business must prepare a separate plan. (Health and SaCety Code Section 25501 (d) aDd 25504). CaliforniA Code or ReRull.tioft!!l leeR). Administrative Code. Cormerly the CaIiCornia California HI.~ardou! Wll~te Control Aet fl972~ the CaliCornia Hazardous Waste Control Act (HWCA)" is one oC, tbe most comprebensive state hazardous waste control prOlramL It authorizes tbe Department oC Health Services to manale hazardous wastes by relulatinl those who lenerate, transport, store, and dispose oC hazardous wastes. The provisions oC HWCA are similar to, althoulb in some case more strinlent than, tbose under Cederal law,' with respect to testinl, Iistinl wastes, maniCestinl. Iicensinl and permittinl dispOsal Cacilities. The act has adopted all oC the RCRA'relulations by reCerence and applies them to all industries that generate any amount oC hazardous waste. Small quantity generators are not exempt Crom this State law. The HWCA is contained in Chapter 6.5 of the CaliCornia Health and SaCety Code, with regulations in Title 22 oC the CaliCornia Code oC Regulations. California Waste Exchaue: a system coordinated througb the State Department of Health Services Cor information sbarin& between hazardous waste generators and other firms to Cacilitate the transCer oC wastes Crom the generator to commercial recyclers ,and other businesses wbo may use the wastes as raw materialL e CaDac:;tv Exc:en or ShortCall' tbe needs assessment compared to tbe existinl capacity. Cement Kiln Incineration' the burning of organic wastes as a supplementary fuel at very high temperatures during the production of cement. .' CEOA: the CaliCorniaEnvironmental Quality Act oC 1970. Tbe act sets forth procedures Cor evaluating a projects impact on the environment. CEOA Guidelines' guidelines developed pursuant to CEQA by the Orfice or the Secretary Cor Environmental ArCairs wbich describes in detail the requirements Cor the preparation or environmental reports in CaIiCorniL ComDrehenlive Environmental Relnon!le Comben!tlltioft a.nd Liabilitv Aet 11980\ ICERCI.,A ): commonly known as "SuperCund", establishes a fund to ensure that fundina is available to cover tbe costs associated with tbe Cleanup or' abandoned waste sites and response to emergency situation CERCLA was amended in 1986 by the SuperCund Amendments and Reauthorization Act (SARA). SARA extends tbe program establisbed under CERCLA ror Cleaning up hazardous waste sites, includinl Cundina Cor cleaninl up leakinl underlround storale tanks and sets more strinlent standards Cor remedial actionL SARA Title Ill, known as tbe Emerlency Plannina and Community Rilht' to Know law requires businesses tbat handle materials to submit inCormation to various alencies. The inCormation ~ . ..-/: A-2 -' . e e e . . reQuired includes emergency planning for extremely hazardous materials, notification of incidents, Community Right to Know Inventory Reporting ReQuirements, and Toxie chemical release reporting (non-accidental emissions). Chemical Treatment. treatment processes which alter the chemical structure of hazardous waste constituents to produce an innocuous neutralization, precipitation, ion exchange, chemical dechlorination, and chemical oxidation/reduction. Chronic' an effect which continues over time. Class I Land DisDosa] Facilitv' a land disposal facility which must conform to the reQuirements of the State Water Resources Control Board for Class I units, and which must be located where .natural geOlogic features provide OPtimum conditions for isolation of wastes from the waters of the State. Currently, these facilities may accept solid and dry hazardous waste. After 1990, they will be precluded from accepting any untreated hazardous wastes. Class I land disposal facilities must conform to the siting criteria established for land disposal facilities in this Hazardous Waste Management Plan. Class I! Land Di,nosal Facilitv: a land disposal facility which must be located where site characteristics and containment structures isolate wastes from the waters of the state. Class II land disposal facilities are suitable for wastes which have been granted a variance from hazardous waste management reQuirements pursuant to Section 66310, Title 22. CCR.. Class II! Land DisDosal Facilitv"a land disposal facility for non-hazardous waste inCluding garbage,' trash, refuse, paper, ashes, etc.. provided such wastes do not contain hazardous or designated wastes. Class III facilities mUSI conform to the reQuirements of the State Water Resources Control Board as specified in Subchapter IS of Chapter 3, Title 23 of the California Code of Regulations and must be located where site characteristics provide adeQuate separation between the waste and the waters of the State. (Also called municipal or sanitary landfill.) Clean Air Act (1970)' The Clean Air Act (CAA), amended in 1977, is designed to protect the public health and welfare from harmful effects of air pollution. The act reQuires the development of National Ambient Air Quality Standards and National E.mission Standards for Hazardous Air Pollutants. The Clean Air Act is applicable to air pollution from facilities such as hazardous waste incinerators. Clean Water Act (1972): The Clean Water Act {CWA), amended in 1977, eliminated the discharge of unregulated pollutants into navigable waters. It contains several provisions dealing with the control of toxic pollutants. One of the most important is the regulation of discharges into surface wa ters through the establishment of the National Pollutants Discharae Elimination System (NPDES). In California, these permits are issued by the Regional Water Quality Control Boards (RWQCBs). Provisions of the CW A limit the concentration by establishing numerical standards which A-3 ".. O' .. . specify the maximum concentration oC a pollutant. e Cleanun Wute~' hazardous wastes associated with the cleanup of contaminated sites. / Conditional U~e Permit. a discretionary permit issued by cities and counties, which is required Cor certain projects that arc allowable by special permit only. A conditional use imposes conditions on a project which arc designed to auure that theproject"is compatible with the local Beneral plan and zoning ordinances and that adverse impacts to neighboring land uses arc minimized. Corrosive: the ability to eause destruction oC livinB tiuue or stcel surCaces by chemical action, CCR., Title 22, Section 66032. CHWMP: County Hazardous Waste Management Plan. The Plan prepared by the County oC San Bernardino in response to AB 2948 (Chapter 150.4, Statutes oC 1986) which directs the manaBement oC hazardous waste. Criteria Air Pollutant: pollutants Cor which the Environmental Protection Agency has published a Criteria Document and which arc reBulated under the Cederal Clean Air Act. Criteria pollutants include: PMIO' ozone, oxides oC sulCur and nitrogen, and carbon monoxide. Deen Well In ;ection: subsurCace emplacement oC fluids throuBh a bored, drilled, or driven well; or through a dug well, where the depth oC the dug well is Breater than the largest surCace dimension (CCR, Title 22, Section 66224). e 'i Develonment CDde" See ZOlliDI ordinaDCC. Diseretioft1lrv Proieet or Permit: a project or permit that requires the use of judBement or deliberation when the public aBency or body decides to approve or disapprove a particular activity, as distinguished Crom situations where the public aBency or body merely has to determine whether there has been conformity with applicable statutes, ordinances, or regulations (i.e~ ministerial permits). Public hearinp arc conducted Cor" discretionary projccts. Disnosal facilitv: a Cacility or part oC"a Cacility at which hazardous waste is intcntionally placed into or on any land or watcr, at which waste will remain after closure (Ca, Title 22, Section 66Q4.C). llllS.; the State Department oC Health Services. The State oC California aBency responsible Cor overseeing the preparation and implementation oC county hazardous waste management plans. Dowftl!radienr: lower phreatic surCace with hydraulic continuity. Environmental ImDact Renort (EIR)' a detailed statement prepared under CEQA describing and analyzing the significant environmental efCects oC a project and discuuing ways to mitigate or avoid the eCCects. e /; -.----"-/ A-4 e e e . . Eft..; Environmental Protection Alency. The Cederal agency responsible Cor implementing Cederal environmental laws. Extremelv Hazardous. Material' a substance or combination of substaDces which. iC human exposure should occur. may likely rcsult in dcath. disabling personal injury or serious illness caused by the substance or combination oC substances because DC iu quantity. concentration, or chemical characteristics. CCR, Title 22, Section 66060. Extremelv Ha:z:ardous Waste' any ha:z:ardous waste or mixture oC ha:z:ardous wastes which. if human exposure should occur. may likely result in dcath, disabling personal injury or serious illness caused by the ha:z:ardous wute or mixture oC ha:z:ardous wastes beca,!se of iu quantity. concentration, or chemical characteristics. Health and Safety Code, Section 2SllS. General Plan' a plan required of counties and cities pursuant to Section 6S300 eueq. of the California Government Code (Title 7: The Planning. Z.oning. and Development Laws) which defines long term planning objectives and policies and serves as a guide Cor local decision-makers. Required elements of the plan include: Land Use, Transportation. Housing. Conservation. Open Space. Seismic Safety, Noise, Scenic Highways, and Safety. Optional elements. such as a Ha:z:ardous Waste element, may also be added to the plan. Generator' any person. by site. whose act or process produces ha:z:ardous waste identified or listed in Article 9 or II DC' Title 22, California Administrative Code. or whose act first c:.:uses a ha:z:ardous waste to become subject to regulation. CCR. Title 22, Section 6607g. Groundwater: water below the land surface in a :z:one of saturation (CCR. Title 22. Section 66079). Habit3t~ or Threatened or Endan2ered SDec:ies' areas known to be inhabited permanently or seasonally or known to be critical at any stage in the life cycle of any species of wildlife or vegetation identified or being considered for identification as "endangered" or "threatened" by the U.S. Department of Interior or the State of California. HaloRenated: substances having a chlorine. bromine, fluorine, or iodine atom in their structure. In general, halogenated compounds tend to be more environmentally persistent and more toxic than non-halogenated compounds. Ha:z:ardous Material: a substance or combination of substances which. because of its quantity. concentration, or physieal, chemical or infectious characteristics. may either: (I) Cause, or significantly contribute to an increase in mortality or an increase in serious irreversible. or incapacitating reversible, ilIn ess; or A.S . . . (2) Pose a substantial prClCnt or potential hazard to human bealth or environment when improperly treated, stored, transported or disposed of or otherwise manaled. Unless expressly provided otherwise, the term "hazardous mater ill" shall be understood to also include extremely hazardous material. (CCR., Title 22, Section 66084.) Ha~ardnu! Material Transftortlltiofl Aet (1974\. the Hazardous Material Transportation Act (HMTA) provides for the relulations of hazardous materials which are transported by air, water, rail, or hilhway. It IUthorizes the Department of Trtnsportation (DOT) to issue rcquiremenu for the paCKalin&, labclin&, and transport of all hazardous material shipments. Hazardou! SubrtBneeo (a) any substance desilnated pursuant to Section 1321 (b) (2) (A) of Title 33 of the United States Code. (b) any element, compound, mixture, solution, or substance desilnated pursuant to Section 102 of the federal act, 42 US.C. 9602. (c) any hazardous waste having the characteristics identified under or listed pursuant to Section 6921 of Title 42 of the United States Code, but not inCluding any waste the regulation of which under tbe Solid Waste Disposal Act bas been suspended by act of Congress. (d) any toxie pollutant listed under Section 1317 (a) of Title 33 of the United States Code. . (e) . any hazardous air pollutant listed under Section 7412 of Title 42 of the United States Code. (f) any imminently hazardous chemical substanee or mixture with respect to which the Administrator of the United States Environmental Protection Agency has taken action pursuant to Section 2606 of Title 15 of the United States Code. (g) any hazardous waste or extremely hazardous waste as defined by Sections 25117 and 25115, respectively, unless expressly excluded. Health and Safety Code Section 25316. ""Il,zardou! Subrttlnce Account Act (Carbenter . Preslev . TaD"!!!") (191] }= this Act, the so called 'state superfund," provides response autbority for hazardous substance releases, inCluding spills and bazardous waste disposal sites. It provides a limited amount of funding for investigation and cleanup of existing and abandoned hazardous waste sites. Sites which may pose a threat to public health and tbe environment are categorized and prioritized for fundine. Funds are also allocated for purcbase of equipment for local hazardous materials prOlrams. . A-6 e "\ e e . . Hazardr>>u~ Wane" a waste. or its quantity. conccntration. charactcristics ma y cithcr: combination oC wastcs. which bccausc oC or physical. chcmical. or inCcctious (a) causc, or significantly contributc to an increasc in mortality or an incrcasc in scrious irrcvcrsiblc, or incapacitating rcvcrsiblc. illncss. (b) posc a substantial prcscnt or potcntial hazard to human hcalth or cnvironmcnt whcn impropcrly trcatcd, storcd. transportcd. or disposcd oC. or othcrwisc managcd. Unless cxpressly providcd othcrwisc, thc tcrm "hazardous wastc" shall be undcrstood to also includc "cxtrcmcly hazardous wastc". Health and SaCcty Codc. Scction 25 I J 7. Thc EP A has cstablishcd Cour charactcristics oC hazardous wastc that can be dctcrmincd by tcsts: Ignitability - thc ability to catch firc. or to burst into flamc spontancously or by intcraction with anothcr substancc or matcrial. Corrosivity . thc ability to wcar away or dcstroy othcr matcrials, including human tissuc. Rcactivity . thc ability to cntcr into a violcnt chcmical rcaction. which may involvc cxplosion or Cumcs. Toxicity - thc ability to rclcasc ccrtain toxic constitucnu whcn lcachcd with a mild acid (Extraction Proccdurc or Wastc Extraction Tcst), or dcmonstratc toxicity in animal studics. (CCR, Titlc 22, Scction 66696 Cl.Scq.) Hazardous Waste Control Account. an on-going statc Cund. dcrivcd Crom fccs paid by opcrators oC on and oCCsitc hazardous wastc disposal Cacilitics, which is thc basic Cunding sourcc Cor thc Statc Dcpartmcnt oC Hcalth Scrviccs hazardous wastc managcmcnt program. Hazardous Wastc Control Act. thc California law, cnactcd in 1972, which "'.as the first comprchcnsivc hazardous wastc control law in thc Unitcd Statcs. It cstablishcd thc statc's hazardous wastc managcmcnt program within thc Dcpartmcnt of Hcalth Scrviccs. Hazardous Waste Facilitv: any structurc, othcr appurtcnanccs, and improvcmcnts on thc land and all contiguous land, uscd Cor trcatmcnt, transCcr. storagc, rcsourcc rccovcry, disposal, or rccycling oC hazardous wastc (California Hcalth and SaCcty Codc, Scction 25117.1). Hazardous Waste Landfill. a disposal Cacility. or part oC a Cacility, whcrc hazardous wastc is placcd in or on land that is not a land treatmcnt Cacility, a surCacc impoundmcnt, or an injcction wcll (Titlc 22, CaliCornia Codc oC Rcgulations, Scction 66123). ACtcr 1990. thc disposal of untreatcd A.7 . . hazardous waste. except lolid c:leanup wastes from existinl c:ontaminated sites, in a landfill will be iIlelal (California Health and Safety Code. Section 25179.6) (Also, lee residuals repository.) e Hazardous Waste Manuement: the disposal, handlin&, processinl, storale, and treatment of hazardous waste. (Also see manalement.) Ha~B.rdous Wane Manaoement F:lemen~ that portioD or a GeDeral PlaD tllat deals with hazardous waste. The County'l Hazardous Waste Manalement Plan will become, after adoption by the County and cities. the Hazardous Waste ManaBement Element. Il!nitable' c:apable of beinl set afire, or of burstinl into flame spontaneously or by interac:tion with another substance or material. (CCR., Title 22, Section 66107.) ImDermeable' not permittinl passale or penetration, especially fluids. Incentives' measures, suc:h as low interest loans, tax breaks, etc.. taken by government to stimulate the development and implementation of an objective, such as improved technologies for managing hazardous waste. Incineration: reducing the volume or toxieity of hazardous waste by burninl it at Iligh temperature. e Incinerator' an enc:losed devic:e using c:ontroUed flame c:ombustion, the primary purpose of whic:h is to thermally break down hazardous waste. Examples are a rotary kiln, fluidized bed liquid injec:tion, and a c:ement kiln. Immobile PODulation~ pOpulations whic:h are particularly difficult to evacuate, such as hospitals, nursing homes, schools, prisons, and jails. Inorl!1lnie' the class of chemical compounds usually containing no carbon and derived from non-livinl matter (mineral). Land DisDosal Restriction' refers to California's program administered by DHS, to progressively ban the land disposal of c:crtain hazardous and extremely hazardous wastes. Restrictions have been established for cyanide wastes, toxic metal wastes, acid waste, PCB's, and liquids, sludges, and solid wastes containing halogenated organic compounds. (CCR, Title 22, Section 66900 et. seq.) Land DisDosa! Facilitv: in the context of this CHWMP, land disposal facility refers to land disposal methods and residuals repositories. Land DisDosal Methods: California Code of Regulations, Title 22. Section 66122 defines the land disposal method as consistinl of the foUowinl three cllaracteristics: (I) "Disposal of hazardous waste on or into tile land, includin&, but not limited to, landfill, surface impoundment, waste piles, dec:p. well injection, land spreadinl, and co-burial witll municipal e A-a e e e .. . garbage. (2) Treatment of hazardous waste 00 or in the land such as ncutralization and evaporatioo poods and land farming, where the treatment residues arc hazardous waste and arc not removed for subsequent processing or disposal within one year. (3) Storage of hazardous waste on or in the land such as waste piles and surface impoundments, other than neutralization and evaporation ponds for longer than one year: Landfa.rmin2 (Land ADDlication Land Snreadin2)o . treatment teChnique which involves spreading the waste on land and utilizing evaporation and microbial action to degrade the wastes. Used primarily for crude oil wastes. Landfill' see hazardous waste landfill. Land Use Permit: a permit required by the County Land Management Department and city planning agencies for all new or modified developments or changes of land use. Lane Quantitv Generator' a generator that produccs more than 1000kg (2200 Ibs) of hazardous waste per month (pursuant to RCRA). Lead A2enev' the public agency which has the principal rcsponsibility for carrying out or approving a projecL The Icad agency will decide whetber an ErR or Negative Declaration will be required for tbe project and will cause the document to be prepared. Leachate: any liquid, inCluding any suspended componeots io the liquid, that have percolated through or drained from hazardous waste (Califoroia Health And Safety Code, Section 25199.3). Liouefaction: surface materials that develop liquid properties upon being physically disturbed. Local Assessment Committee' a review group created by a host or abutting community to analyze a proposed hazardous waste management facility as required by AB 2948 (Chapter 1504, Statutes of 1986). Such Committees may have the authority to negotiate with facility proponent (on behalf of the community) regarding the conditions under which the hazardous waste managemcnt facility may be builL Maior Routes' state and interstate divided highways. Man12ement. the systematic control of the storage, transportation, processing, treatment. collection. source separation. recovery and disposal of hazardous wastes. It includes administrative, financial, legal. and planning activities as well as operational aspects .of hazardous waste handling, disposal. and resource recovery systems. A-9 . . Manife!:t' I stlte form which indicates lenerltor. quantity. type of wlSte, Ind disposer of wlSte for elch shipment of bazardous wastes hlndled It off-site facilities. - ,:; , Minor Router. city street, boulevard. or undivided bilhwlY. Mini!terial Pro;eet or Permit: I loverDmeDtal decisjoD involvill& little or no personal judlement by tbe public official as to tbe wisdom or manner of carryinl out tbe project. Tbe public official mcrcly applies tbe Ilw to tbe facu IS prcscnted. mcrcly applies tbc law to tbc facu as prescntcd. but uses no special discrction or judlcmcnt in rcacbinl I deeision. A ministcrial dccision involves only the use of fixed standards or objectivc mClSurcmcnts. and the public official cannot use personal, subjectivc judlcmcnt in dccidinl whctbcr or how.thc project sbould be carricd out. Common cnmplcs of ministcrial permits include lutomotive rClistratiollS, dOl liccnscs, and marrillc lieenses. Mitintion' rcduction of I ccrtlin or suspectcd advcrse implct rcsultinl from a proposcd action by: (a) Ivoidinl the impact altolcthcr by not tlkinl ccrtain action or parU of an action. (b) minimi:tinl impacu by limltinl thc dClree or ma.nltudc of tbc Iction and its implcmcntation. e (c) rcctifyinl tbe impact by rcpairinc. rcblbilitltinl, or restorinl tbe impactcd cnvironmcnt. (d) compcnsatinl for the implct by replacinl or providinl substitutc rcsource!: or cnvironmcnts. Munic:ioal Landfill' see Class III land disposal facility, Netzatjve Dec:laration' a writtcn statemcnt by the lcad Ileney and subject to formal public review wbicb bricfly dcscribcs tbe rcasons wby I proposed project, not cxcmpt from CEQA. will not blve I silnificant cffcct on tbc cnvlronmcnt and, thcrcforc, docs not requirc thc prcparation of an EIIt (Section 15371, CEQA Guidclincs), Need for Facility: I prcscnt or projectcd shortfall of facilities to meet local or multi-county wastc manllcmcnt purposes, includinl facilities which provide more desirablc or cconomic mcans of hazardous wastc manalcment and mlY scrvc relionll needs, Needs Assessment: tbe dctcrmination of tbe total required capacity (trcatmcnt or disposal. dcpendinl on contcxt). tlkin. into considcratIon existinl capacity wbich is likcly to rcmain operationaL Neutralintion: I trcltmcnt tccbnololY whcrc by acids and alkalis are relctcd to form salts and watcr witb I pb approlcbinl ncutral. e A-IO e e ,e ,~> . . Non-attainment Areas' areas in which the level of one or more of the criteria air pollutanu exceeds the National Ambient Air Quality Standards. Nonhal02enated' substances which do not contain halogens (chlorine. bronrine, fluorine, or iodine) and generally evaporate at relatively low temperatures. (Also see halogenated.) orrsite Hazardous Waste F&ci1itv~ an operation involving handlin&. treatment, storage, or disposal of hazardous waste at a site physically separate from the site where the waste was generated; at a site not owned by, or leased to the producer of the waste; or at a site which receives waste from more than one generator. (Also see specified hazardous waste facility.) . Onsile Hazardrms Waste Facilit~ an operation inVOlving treatment. storage, or disposal of hazardous waste on land owned by or leased to the waste producer, at or contiguous to the site of waste gcneration, and that receives hazardous waste produced only by the generator. OnsiteTreatment. treatmcnt of a waste on the site where it was originally genera ted, Ooerator' a person, government unit, or company that conducts treatment, storage, or disposal of wastes of a facility. The operator mayor may not be the developer. Ona n ic' the class of chemical compounds of carbon, primarily hydrocarbons and their derivatives. The name originated from the belief that this class of compounds could be derived only from living organisms (plant or animal), Now many organic compounds are synthesized in .the laboratory. PCB's' polychlorinated biphenyl - any of a group of chlorinated compounds used in industrial processes in the form of colorless, odorless, viscous liquid, and discharged in industrial wastes, Permeable Soils: soils that are open to passage or penetration, especially by fluids. fa; a measure of the acidity or alkalinity of a liquid. The ph scale indicates neutrality at 7; acidity is indicated by numbers below 7. down to zero, Alkalinity is identified by numbers above 7, up to 14. Phvsical Treatment. treatment processes which separate components of a waste stream' or change the physical form of the waste without altering the chemical structure of the constituent materials. Prevention or Sil!nirieant Deterioration Areas: areas in attainment oC the National Ambient Air Quality Standards. Process Substitution: substituting one industrial or prOduction process Cor another, usually in order to reduce the amount of toxic or unwanted material used or produced. A-II . . . Publie Faeilitic~' lands owned by federal. state, county. or local governments on which facilities used to supply public services are located, such as; highway maintcnance and storage areas, airports, city or county corporation yards, waste disposal facilities, sewage treatment facilities, sta te school lands. Raoid Geolol!ic:al Chanc' alteration of the ground surface through such actions as landslides, subsidence. and faUlting (CCR, Title 23, Article 10). RCRA- see Resource Conservation and Recovery Act. RCRA Gencrator. generators producins more than 1000 kg (2.200 Ibs) of haurdous waste per month. Rcaetive' having properties of explosivity or of chemical activity which can be a hazard to human health or the environment. Reehane Area: a land area where raillwater, infiltration from surface strcams or impoundmcnt areas or other sources soak into the sround and enter an aquifer. Reevelilll!' refers to the use or reuse of a waste as all erfective substitute for a commercial product, or as an ingredient or feedstock in a industrial process. It also refers to the reclamatioll of useful constituent fractions within a waste material or removal of contaminants from a waste to allow it to be reused. - . RCl!iollal Plall' a plan prepared by one of the Council of Governments designated in AB 2948 (Chapter 1504, Statutes of 1986) or by a joint agreement between two or more counties under a legally constituted agellcy covering the plannin! area, which has the delegated authority to prepare a Regional Plan. The Southern California Haurdous Waste Mallagemellt Authority is preparing a rcgional plan for the Southern California area. Releue' any spill ins. lcakins, pumping, pouring, emitting, emptying, discharging, injecting, cscaping, leaching, dumping, or disposing of haurdous materials into the environment. Research Develonment and nemon~trltion Unit: ha.zardous waste facilities so designated by the California Department of Health Services. Such facilities arc required to meet the siting criteria identified in this Plan and must be approved through the local permitting process described in th~s Plan. Residuals: materials remaining after waste treatment and/or reduction processes have taken place. Residuals may be less hazardous, less voluminous, or more easily contained than original hazardous waste. Residuals Reoodtorv: a hazardous waste facility which accepts only treated haurdous waste. meets all applicable federal and state regulations, and holds a hazardous waste facility permit. e A-12 e e . . Resource Conservation and Rceoverv Ac:t 1976 lRCRA): a federal statute which gives thc EPA thc authodty to dcvelop a nationwide program to regulate hazardous wastes from 'Cradle to Grave'. The program includes requirements for the use of a manifest system to track the path of the waste, specific record keeping and labeling requirements, requirements for storage of hazardous waste and a permitting system for hazardous waste facilities. RCRA docs not regulate generators of less than 100 kilograms of hazardous waste per month. In 1984, RCRA was amended to expand the regulatory control over hazardous wastes (hazardous and solid waste Amendment of RCRA). The two key clements of the amendments arc; I) a national policy that waste generation is to be reduced or eliminated where feasible, and where it is not possible to eliminate the waste,. it should be treated, stored, or disposed of in a manner which reduces the volume and/or toxicity of the waste, and 2) a program to phase out the land disposal of untreated huardous waste by 1990. Resource Recoverv' the reuse or reclamation of any hazardous waste or any recyclable hazardous material. (CCR, Title 22, Section 66180.) ResDonsible A2encv: a public agency which proposes to carry out or approve a project, for which a Lead Agency is preparing or has prepared an EIR or Negative Declaration pursuant to CEQA. For the purposes of CEQA, the term 'responsible agency' includes all public agencies other than the lead agency which have discretionary approval power over the project. ~ a measure of the likelihood and the severity of injury. Risk Mana2cmcnt and Prevention Pro2ram (RMPP)' all of the administrative and operational programs which are designed to prevent acutely hazardous materials accident risks, including, but not limited to, programs which include design safety of new and existing equipment, investigations procedures, risk assessment for unit operations, or operating alternatives, emergency response planning, and internal or external audit procedures to ensure that these programs arc being executed as planned. Health and Safety Code, Section 25532 (g). Safe Drinkin2 Water Act ( 1974): The Safe Drinking Water ACt (SDWA) is intended to provide for the safety of drinking water supplies throughout the nation by establishing and enforcing national drinking water quality standards. In addition, the act requires the development of an Underground Injection Control program to regulate the discharge of wastes into underground water supplies. Seiches: vertically oscillating standing waves usually occurring in enclosed bodies of water such as lakes, reservoirs, and harbors caused by seismic activity, violent winds, or changes in atmospheric pressure. e Site ADDroval: see Conditional Use Permit. A-13 . . Sitiu Criteria' factors which must be met to determine an environmentally appropriate site or area for the location of oa specified hazardous waste management facility. e Slud2e: waste materials in the form of a concentrated suspension of wute solids. One type of sludge is produCed from the treatment of sewage. Small Ouantitv Generator. a lenerator which produces less than 1000 kl (2,200 lbs.) of hazardous waste. Solidifieation'a treatment process for limiting the SOlubility of or detoxifying hazardous wastes by producing blocks of treated waste with high structural integrity. Solid Waste: all solid and semisolid wastes, such as garbage, rubbish, paper, ashes, industrial wastes, demolition and construction wastes. abandoned vehicles and parts thereof, discarded home and industrial appliances, manure, vegetable or animal solid and semisolid wastes, and other diSCharged solid and semisolid wastes at solid waste transfer jprocessing stations or disposal sites, but eXCluding a)sewale collected and treated in a municipal or regional sewage system; or b) material or substances having commercial value, which have been salvaged for refuse, recycling. or resale. Solvent: a substance used for dissolving another substance. e Sour". ~edu"tion' the reduction or elimination of waste generation at the source, usually within a process. Source reduction measures can include process modifications, feedstock substitutions or improvements in feedstock purity, various housekeeping and management practices, increases in the efficiency of machinery, and eVen recycling within a process. Source reduction implies any action that reduces the amount of waste exiting (rom a process. Soe"ial Waste: a waste which is a hazardous waste only because it contains an inorganic substance or substances that cause it to pose a chronic toxicity hazard to human health or the environment and which meets all of the criteria and reQuirements of Section 66742 of Title 22 of the California Code of Regulations and has been classified a special wute pursuant to Section 66744 (CCR, Title 22, California Code of Regulations. Section 66195). Srteeiried HI.2:llrdou! Waste F.c:ilit~ aD orrshe hazardous waste (acility which accepts wastes from more than one producer of hazardous waste (California Health and Safety Code, Section 25199.1 (m)). For purposes of this Plan, a HOUSehold Hazardous Waste Collection Center with a capacity of less than SO drums of waste is not considered a specified hazardous waste facility. Sneeiried Ha2:ardous Waste raeilitv Overlav Zone- aD overlay lODe that can be applied to Resource Conservation and Regional Industrial Districts (or eQuivalent desert or heavy industrial zones) to allow and specify the e: A-14 e e e . . requirements for the siting of specified hazardous waste facilities. The overlay zone is not given a specific location until it is applied to a specific site upon approval of a project. Sta biliza tion: a treatment process for limiting the solubility of a detoxifying hazardous wastes by adding materials which ensure that hazardous constituents are maintained in their least soluble and/or toxic form. Standard lndu!;triat Cla!sirication (~lC) Code' an idcntiricatiOD Dumber assigned to specific types of businesses which systematically classifies all economic activities in the United States, dividing them into groups and subgroups. Major groups are assigned two-digit numbers and they are subgrouped into three and four-digit numbers. The United States government publishes The Standard Industrial Classirieation Manual which lists and describes all SIC Code Classifications. Storaee' the containment of a hazardous material or hazardous waste, either temporarily. or long term, in such a manner as not to constitute disposal or use of such material. (California Health and Safety Code, Section 2S 123.) Storaee Facili'tv: a hazardous waste facility at which hazardous waste is contained for a period greater than 96 hours at an orr-site facility or for periodS greater than 90 days at an on-site facility. Health and Safety Code Section 2S 123.3. Subsidence: a. sinking of the land surface fallowing the removal of 'Solid mineral matter or fluids (e.g., water or oil) from the subsurface. SUDerfund: refers to federal and state funding mechanisms and progralllS, the primary purpose which is to clean up hazardous waste sites that pose a threat to public health. Surface ImDOundment. a facility or part of a facility which is a natural topographic depression, man-made excavation or diked area formed primarily of earthen materials (although it may be lined with man-made materials), which is designed to hold an accumulation of liquid wastes containing free liquids, and which is not an injection well. Examples of surface impoundments are holding, storage, settling, and aeration pits, ponds. and lagoons (CCR, Title 22, Section 66200). Surficial Materials' geologic materials at the earth's surface. Toxic' capable of producing injury, illness, or damage to humans, domestic livestock, or wildlife through ingestion, inhalation, or absorption through any body surface. Toxic Air Contaminant: those substances identified by the Air Resources Board as air pollutants which may cause or contribute to an increase in deaths or serious illness or which may pose a present or future hazard to human health. A-IS . . e Toxie Pit! CleBnu" Act (1984): the Toxic: Pits Cleanup Ac:t (TPCA) established restrictions for hazardous waste discbarle into surface impoundments. Cleanups arc required of any impoundment wbich may c:ontaminate water rcaourcca. All other impoundments are required to have double liners, leachate collection, and Iroundwater monitorinl systems. The TPCA is implemented throulh the State Water Resources Control Board. .--; Toxie Sub~tance~ Control Act (1976)' The Toxic Substance Control Act (TSCA) is designed to provide control over toxic chemfcals before they enter the stream of commerce. It requires pre-manufacture notification (PMN) for all new chemicals and for silnificantly expanded uses of existing chemicals.' PMNs detail existinl information on hcalth and environmental effects and allow EPA to limit or prohibit a chemical's use if it poses an unrcasonable risk to human health or the environmenL TSCA also authorizes EPA to develop I comprehcnsive inventory of existinl chemicals and to require testinl for those thlt appelr to pose In unreasonable risk. - Toxie Waste' I waste which can produce injury upon contact with or by ac:c:umulation in I susceptible site in or on tbc body of I livinl orglnism. Tran~fer Stllt;on' any hlzardous waste facility where hazardous wastes arc loaded, unloaded, pumped or packaled (CCR., Title 22, Section 66212). e Tr8n~nortabJe Treatment Unit: hazardous waste treatmcDt works which are designed to be moved either intact or in modules Ind which are intended to be operlted It I given location for I limited period of time. Treated HnBrdou~ Waste' the residual portion of I hazardous waste thlt is produced when the hazardous waste is treated by I method. teC:hnique, or proc:ess, inC:luding incineration. that changes the physical. chemical. or biOlogical character or composition of the waste and that is in compliance with at least one of the fol1owinl: (California Health Ind Safety Code, Sec:tions 2S 179.3(1). 2S 179.6.) It meets the criteril and requirements for, and may be managed as I spec:ial waste pursuant to Sec:tion 66744 of Title 22 of the California Code of Regulations. It docs not contain Iny persistent or bioac:cumulltive toxic substance in exc:ess of the soluble threshold limit concentration for the substlnce' as established in relulatioDS adopted by the Stlte Department of Health Services. It meets treatment standards estlblished by the Environmental Protection Agency pursuant to subsection (m) of Section 201 of the Hazardous and Solid Waste Act Amendments of 1984 {Title 42, U.s. Code. Section 6924 (m)) or, if the State Deplrtment of Health Services has established equivalent or more stringent treatment standards, it meets the treatment standards established. - / A-16 e e e . . Treatment. any method, technique, or process which changes the physical, chemical, or biological character or composition of any hazardous waste or any material contained thcrein, or removes or reduces its harmful properties or characteristics for aDY purpose. (California Health aDd Sa f ety Code, Section 25123.5.) Treatment Facilitv: any facility at which hazardous waste is subjected to treatment or where a rcsource is recovercd from a hazardous waste. TSDF' a trcatment, storage and disposal facility. Vadose Zone: the unsaturated arca between ground surface and the water table. Volatile' a material which vaporizes or evaporates quiCkly. Waste: any material for which no use or reuse is intended and which is to be discarded; or a material which must be treated in some way (i.e~ recycled) prior to reuse, Waste Exchanl!e' clearinghouse approach to transferring treated and untreated hazardous wastes to an industrial user for use as raw material. Waste exchange is one method of waste minimization. (Also, see California Waste Exchange.) Waste Minimization' the reduction, to the extent feasible, of hazardous waste "that is generated or subsequently treated, stored, or disposed of. Il includes a source reduction or recycling activity undertaken by a gcnerator that results in either (I) the reduction of total volume or quantity of hazardous waste, or (2) the reduction of toxicity of hazardous waste, or both, so long as the reduction is consistent with the goal of minimizing present and future threats to human health and the environment. Waste Pile: any non-containerized accumulation of solid, non-flowing hazardous waste that is used for treatment or storage (CCR, Title 22, Section 66160). Wastestream' all waste coming into, through, or out of a facility; sometimes used to rcfer to all waste collectively. Wastewaters' water carrying dissolved or suspended solids from homes, farms, businesses, and industries. Well Fields: areas used for extraction of groundwater for drinking water supplies by high capacity production wells and identified by the presence of several wells that constitute a well field. Wetlands: areas such as saltwater, freshwater, and brackish marshes, swamps, and bogs inundated by surface or groundwater with a frequency to support, under normal circumstances, a prevalence of vegetative or aquatic life that requires saturated soil conditions for growth and reproduction, A-I' . . ZoninR Ordinancc. the let or ordinanccs developed by a local juri.dic:tion that de.ianlltes allowed UICI or all areu in the jurisdic:tion. The Zonina ordinanc:cs are auided by and support the objcc:tivcs spec:iried in the General Plan. (The County or San Bernardino refen to its zonina ordinanc:es as the Development Code.) e e e / , A-II . e APPENDIX B LEGlSLA nON REGARDING HAZARDOUS WASTE MANAGEMENT e ,e , . lie e e > .. ... il o z t': == 3" ;: .. M M < i - c=c:,=~; "o=.:l'lo e:"eu-'l:I E~eJl::l5 ~~ ..,. >"'C 0": C..c C"':l~:: c ",._~=o 1:1." Cot- ~ _co; IIC&I lie '="':&1.5"'.- - C~ uii-= 0"-=". -,..: ": i Ci."ij e-<=u", g~:g~i.; ~ s :"!::"fu5 --.... ''l:I u .....;... 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'I f S 'OlI-:l~~-j - ~jjll:l~i . c; F=-S~~ s U.a I .' . . e 1987-1988 REGULAR SESSIOS Ch. 1167 (b) Except as provided in subdivision (al. any personnel of the multidis~iplinary team that rec:ei\'es information pursuant to this chapler. shall be under the same obligations and subjec:tto the same confidentiality penalties as the person disc:losing or providing that ,nfom.tion. The information obtained shall be maintained in a manner that ensures the maximum prote~tion of privacy and confidentiality rights. SEe. 8. This a~t is an urgency statute necessary for the i/Ilnlediate preservation of the publi~ peace, health, or safety within the meaning of Article IV of the Constitution and shall go into unmediate effec:t. The facts ~onslituting the necessity are: In order to apply the requirements of this ac:tto the administration of the model proje~ts in the most et'Onomic:al and effic:ient manner, it is nec:essary that this a~t take effe~t immediately. HAZARDOUS SUBSTANCES A!\D WASTE-SOLID WASTE 1I1ANAGEME1\'T PLAN-FACILITIES Senate Bill 1\0. ~77 e CH.....PTER 1167 .....n aet to amend Se~tions 25135.1 and 25135.7 of the Health and !..fet)' Code, relating to hazardous waste. IAppro,,~d ",. CO\'emOr Septemb.r 25. 1m. l'iJeod ,,'ilh ~r~t"r of SIa.. ~p'enlber 26. Im.J e J..E:CISl..'T1VE COt:~SEl.:S DICEST SB ~77. B. Greene. Hazardous waste management plan. III Existing la'" authorizes a c:ounty, in lieu of preparing the r_z.,dous wlIste portion of the solid waste management plan, or a tot). ~s specified. to adopt, b)' September 30, 1988, a hazardous ,,'aste ~..Il.gement plan pursuant to guidelines adopted by the' State 0, ".rtment of Health SeT\ices, and specifies the procedure. for the ;,:('p~ration, re\;sion, adoption, appro\'al, and amendment of these ;...ns. The plan is required to inc:lude spec:ified elements, inc:luding _t. ,dentification of general areas or spec:ifi~ sites for new haurdow '.; .'Ie facilities determined to be needed. Within 90 da)'s after the :'p.rtment appro\'es a plan, the ~ounl)' is required to incorporate ::.,. plan into the: c:ounty's general plan or enaet an ordinance :'. ,;Ilring th~t spe~ified land use decisions be c:onsistent "ith the ;.':!l. . This bill would delete the identific:ation of specific: sites for new ;-;,hties from the elements required to be included in the plan. The ~.'i would extend this go.day period to 180 days, and would require ,:., ordin~nc:e enac:ted b)' the c:ounty to require that land use ~""'ons be t'onsistent with the portions of the plan whic:h identif)' '.,.,..f'l: sites or siting c:riteria for hazardous waste facilities. The bill ....Id also require eac:h c:it)' v,;thin a t'Ounty that has an appro\oed ""'1 " k\cIle8t.. ,,11 ...&ellon 1007 . . e Ch. 1167. STATL'TES OF 1'81 , plan 10 adopt a cit)' ha7.ardous ,,'ute management plan. incorpor.l the plan into the cit)"s seneral plan, or enllct an ordinanee Tf.quirin; that land use decisions be eonsistent \\ith the specified portion of tilt- plan. thereby Imposing I state-mundated loeal pro;rllm. The bill would specify thllt these pro\isions do not limit lilt- authorit)' of II cil)' to lIIke speeilied actions eoneenllng land \lW' apprO\'als. plllllnlng requirements. or siting criteria. (2) The California Constitution requires the Stlltf' to rf'hnbuh(' local agencies and school distriets for certllln eoslli mllnc\;ltt'd b\. thr state. StatutOf')' pro\isions e~tllblish proeedurf'S for In:lkin~' tlwt reimbu~ment, ineluding the creation of II Stllte ~lllnc\;ltt'S Cluil1b Fund to pu)' the eosts of mllndlltes which do not ecteet'd S5OO.ooo state\\ide and other proeedures for elllims whOll(' 5tatc\\idt' ~\" exceed SSOO.OOO. This bill would pro\ide thllt. if the Commission on Stlllt' :\hmdatt'\ determines thut this bill eontllins costs mundatt'd by tht' Slutl'. reimhllrSf'menl for those costs shall be made pursuant to thow stilt\1torr proeedures and, if the state..ide cost does not exceed S5OO,OOO. shall be mllde from the State ~landa~es Claims Fund. Thf' ~p/f' of the Stlltf' of CWfomia do elUlc:t u foJ/on: SECTlOX 1. Section 25135,1 of the Health and Safety Code is Ilmended to read: 25135.1. (a) For purposes of this article, and unless the context indieutes othen\ise. MeountyM means a eounty that notifies the department that It will prepare a eounty hazardous waste i'll.1n:lJt'ment plan in a=danee ..ith this artiele and reeei\'eS a gnmt pursuant to Section 25135.8. MCountyM also means any e1ty. or t\\'o or more e1ties ..ithin a eoun~' acting jointly. whieh notifies the dep:lrtment that it ..ill prepare a eounty hazardous waste management plan in aeeordanee \\ith subdivision (e). (hI .0\ eounl\' mn. at its discretion. and after notification to the department. p~;e a county hazardous waste management plan for the manllgement of all hazardous lI.'&Ste produced in the eounty. .0\ eountr hazardous wllSte management plan prepared pursuant to this article shall sen 'e in lieu of the hazardous waste portion of the county solid waste plan pfO\ided for In Article 2 (eommencinlll.;th Section 667801 of Chapter 2 of Title 7.3 of the Go\oemment Code. The cowlty hazardous waste manasement plan shall be prepared in cooperlltion \\ith the afl'eeted cities In the eounty and the ad\iso~' committee appointed pursuant to Section 25135.2, in aeeorclanee ,,;th the guidelines adopted b)' the department pursuant to Sec:tion 25135.3. Ilnd in aeeordanee ..ith the schedule specified in Sec:tion 25135.6. (cIOn or before ~lareh 31. 1987. e\'ery eount)' shall notif)' the dep:lrtmf'nt und the e1ties \\ithin the eounl)' whether the eounty has elect...d to preparf' a eount)' haZllTdous waste management plan pursuant to this artiele. .10 e1tr. or two or more cities acting jointl)'. 1000~led u;thin a count)' which elects not to prepare a eoun~' hIIZ>lJ'dous \\'IlStf' m'UllIgement plllll or whieh fails to makf' an election. on or before ~llITch 31. 1981, to prepare a plllll. ma~'. at tht eitr's or eitif'S' diserf'tion. elect to undert:alce the prepaflltion of tht e e 1008 C1wft'.. or .._III....... _.. ~ _- . . ..... >.- 1987-1988 REGliLAR SESSION Ch. 1167 e pl:m. Thl." C'it~. or C'itil."S shnll be." dl."l."ml."d to be." ilC'ting in plilC''' of the C'ollnt~ for pnrposl."s of this ilrtiel.. und mill' npply for funding to pill' \h.. C'OS\ of prC'parin" th.. pllin pursnanl 10 sllbdhision (C') of Sl."C'tion 15135.8. Ho\\'l."\ ..r. thC' C'it~. or C'itit's may not rl."C'C'i\'.. fnnding pnr<n""t 10 subdhision IC') of Sl.",'tion 251:15.8. nnlC'5s the prnpo~IIIO prC'p.u.. a C'Ollllty hausrclous ","ste miln:t!!l."mC'nl phll1 by thC' C'ity or eiti..s is .lppro\'C'c1 b~' II mlljorily of th.. C'iti..s \\.ithin thC' C'olmty ",hiC'h C'ontilin " m:tjority of thC' popnlJtion of th.. inC'orporalC'd ilrC'il of the- C'Ollllty .lIld IhC' I>ropo-;.I is r..C'C'i\ C'd b~' thC' c1C'p:lrtmC'1l1 on or bC'forC' Jnn.. 30. IlISi. ld I ThC' C'ollnty h:l"lIrdom \\'.I<IC' m.uI:ll!C'ml."nl phm 'IlIthori7...d by .ubdi\'i.ion (1.11 or IC'I .h:lIl.C'Tl'C' 'Is thl." primary planniug dut:lIIn"nl for h.l:tolrnous wm,h' m;IIl.I~t-nlC"n~ in tht." county und )hall bt- pre-par..d ,I> .. n...ful infol'ln:tliun..1 .onr,... fur loc,.1 !!o\'C'rnu1C'nl :lnd Ihe' public. Ti,e' pl:1Il sh:lll induM. bul is not limi\l>d tu, all uf Ih" follo\\in!! dt"m..nts: III ....n ,m:tl~..i, of IhC' h:t~';lrdom ",a.tC' strC'iun g..n..ra\l'tl ill th,- C'Ol1nty. includinp; .01 ;Ic."counling of the ,.ohllnt.'!! uf hm'.,""rdoll~ \\";t!'rlt(.~ produC'l."d in the- C'Onnty"- by t~.p<' of \\....t.... :lnd C'stin",\". uf th,' "xpe'C'lt.d ral... of ha:L:lrdollS \\'asl,> prodllC'tion unlil1!1!1~, by I~'P" uf Wolst~. (2) .... d..sC'riplioll of thC' l."xisling h..z:trdou. \\';1>1" faC'iliti... \\'hic'h trl."al. handll.". r..C'yell.". ..nd disposC' of the' ha:L:lrdon. wast..s proclu,...cJ in Ih.. C'ount~.. inelllding a dC'\l."T1nin:ttion of Ih.. ..xisling C'apaC'it~ uf e-aC'h facilit\.. (3) ....n ~nalysis of thl." potl."nlilll in thl." C'ounty fur r"C'~'C'linl! hilurdous "'lIste llnd for reduC'ing th.. ,"ohmIC' lInd h'LZilrd of haurdous ""lSte at thl." SOllrC'e of gen..ration. (4) .... C'on.iderntion of th.. need'to mllnllgl." thl." .,nall \'ohlmf'. of haurdous wastl." produC'ed by businesses and housl."hold.. (5) A determination of the n..ed for additionlll haurdollS "':I.tC' facilities to properly managl." thl.". \'olumes of ha:L:lrdous \\,asl..S C'uTTently produC'ed or that are e''peC'ted to be." prodllC'ed during thf' planning period. (6) An identifiC'ation of those ha:<llrdous ",aste facilities th,lt C'an be e''Panded to accommodate projeC'ted needs and an idl."ntifiC'ation of general areas"for ne\\' haurdous waste facilities determin..d to bt" nl."l."ded. In lieu of this faC'ilit)' and ~ identification, the pl~n mllY instead indude siting C'riteria to be utili:Led in seleC'ting sites for ne\\' haurdous waste faC'ilities.If siting C'riteria are induded in the C'ount~. haurdous waste management plan. the plan shall also designatl." general areas where the C'riteria might be." appliC'able. (7) A statement of goals. objeC'ti\'es. and poliC'ies for thl." siting of haurdous waste facilities and the general management orhuardous wastes through the year 2000, (8) .~ schedule whiC'h describes count). and citr aC'tiom neC'essurr to implement the haurdous waste management plan through th.. year 2000, induding the assigning of dates for c:aTT)ing out th.. aC'lions. (e) In addition to the elements of the plan required b}' subdilision (d). a c:ount!' may inC'lude a desC'ription of IIn}' additional local progr~ms whiC'h the C'ounl)' determines to be." neC'eSSllr~' to pro\idC' for the proper management of haurdous wastes produced in th.. e '-'. 'rmbol .. IIIlllcol.. lOll __ 1009 . . e Ch. 1167 STATUTES OF 1981 -,' county: These programs may Inc:1ude. but are not limited 10, publ, education. enforcement, surveillance. trllflsporlallon r administration. . on~ <0 The inc:1usion of an element in a county hazardous Wo I management plan pursuant to subdhision (d) or (e) d~ I~ authorize the county to adopt a program which the counh' is not othe"';5(' uuthorizt'd 10 udo!'t under unr other provision of Law SEe. 2. s..'C:tion 23135,7 of the Ileulth ,md S"fety Code is IImend.u to re-old: 23135.7, ,u'," countr ~hull ~ubmil the finul t'Ountr haZilrdOlb ",ustC' m:lIlu~ement plun IIdoptr-d b)' the count)' to the depurtlnent for r..'.j....... und uppro,'ul on or before Octnber 1. 1988. If II COllnt' mo\\'s the dC'purtment thut th.. county h~ made ~ubst:lIltiul progrhl to...urcL. cuJnpleting the count)' huzurdo\l' \\'uste mwlugemenl plan und nC'r-ds more time to complete the plnn. thC' depurtment 11\;1. extend this cIo.te to Februurr 1. 19119. The depurtmcllt ~h.1l1, on or befure December 31, 1988. or on or before ."pril 30, 19811. if th. count)' Is gh'en a time extension. re,;ew' and either uppro"c or disuppro"e the countr huzurdous ",u~te munagement plun. n,.. depurtlnent shull appro,'e the count). huzurdous \\'uste munur;ement plan if the dep.lrtment muke~ ull of the follo\\;ng determination$: (1\ The plun substl1lltiallr complies ,,;th thC' guidelin~ for tht' prepur'ltion of hlIZ1lfdous \\';lSte management pluns adopted br the department. (2\ The plun applies the methods. techniques, Imd polioc. established b)' the department to analrze the ,.,uste stream and t~ determine whether there is a .need for additional or eEpIIDdPd hazardous waste r.Jcilities to SlIfely manage llfId propen)' dispow' of the hazardous waste generated within the count)" (3) if the plan contains a determination PUrsullflt to paragraph (5) of subdhisiol'l @ of Section 23135.1 thaI there is II ne-ed for additiunal or expanded hazardous waste facilities, the plan proposes general areas, or. as determined appropriate by the count)'. proposes specifie sites which may be suitable locations for a facility. Howe,'er, if the plan instead contains siting criteria for selecting sites for ne\\' hazardous waste facilities. the plan shall propose general are:lS where the criteria might be applicable. (4) If the county preparinl the plan has entered Into a formal agreement v.;th other counties to manage hazardous waste. the agreement is documented. (b) Within !E days after the department appro"es a county hazardous waste management plan. the county shall either incorporate the applicable DOrtions of the plan, b)' reference. into the county's general plan,. or enact an ordinance which requires that aU applicable zoninl. subdivision. conditional use permit, and ,'ariance decisions are consistent with ~rtlons of the coun~' hlIzardous waste management plan which Identify stlecific sites or sitinl! critC'"~ for hazardous waste facilities. (c) Within 1~...9.m.~er rec:eMnl! writt'!!n notification from the deoartment'iliat it has a royed the coun hazardous ..-aste m&nal!ement 'Plan. each city ..;t in that county shall do one of the followinR: e. e 1010 C"",,,.' Dr .cldlllOn. 11111&1 ... IncII"locI", .......rIll!! . . e e 1987';'1988 REGULAR SESSIOS Ch. 1168 (I) Adopt a eitl' hazardous waste mana~ement plan eontainin~ all cilht..elem~~!eQuired bnubdivision (d) ofSeetion25I:!5.J w ieh shull be eOl\sistent ,,'ilh thc uppro\'C.d t'OUllt\" hu,.ardou. waste nhu'mszelnent p!.lI1. - (2) Il!corpomle the applic:ublc portions of the appro\Oed counh' Ehm, b.t~f~~!l~' inlO the cit .'s encruT"i)1an. (~Emlel an ordin:mee whie re nires thulall :l Iic:uble 7.onin subCIT\ ision. c:oliOitiC:\nu ust"' permit. and nlriancc C'cisjol\S UTe consistent ,,;th the \)ortion. of the II ro\'ed enllnt\" hill whieh j,Q;nlif\" ~eneml areas or sjtill~ erileri. for h:l:t:lr ous wl1>1e f;lc:ilities. (d I This seetion doe. not limit the lluthorit . of all\" cit\. to :llllleh oJPPToprhltt- conditions to..!.. e- issm.mc.-eo 0 un\' an lI)t" iJDPro\"ill for ;1 hll"urdous wilsle f;,eilit\. ill order to protect the public: health, "lfet\.. or welfare, IInd doe. nJ?t limit the allthont\" of a eit\. 10 establish more strill~ent planninR reQuirement. or .itillR erileri;, thull those sJ>eeified_i!l the county haUlrdolls "'lIsle mllllu~ement plan. !.tl. .'\n)' amendment to an adopted eountr hilUlrdolls wasle milnnp;ement pllln requires the appro\'lll of the depllrtment, the count)', Mnd a majority of the eities ,,;thin the count)' "..hich contain a m~ority of the ?O?Ullltion of the ineoT?orilted are. of the collnt)'. SEC. 3. !'\otwithstanding Seetion 17610 of the Covernmenl Code. if the Commission on Stale Mandates determines thaI this aet eontains eosts mandated by the state. 0 reimbursement to loe..l agencies and school distrlets for those costs shall be made pum.anl to Part 7 (commencing with Seetion 17500) of Division 4 of Title 2 of the Government Code. If the statewide cost of the elaim for reimbursement does not exeeed five hundred thousand dollars (SSOO,OOO) , reimbursement shall be made from the State Mandotes Cairns Fund. STATE FIRE MARSHAl-DUTIES- STATUTORY YIOLATIONS Senate Bill No. 531 CHAPTER 1168 e An aet to amend Seetion 13142.4 of, and to reJ>Cal Seetion 13254 of, the Health and Safety Code, relating to the State Fire Marshal. (Approved by eo- September 15. les7. raW .ilh SeerelU)' cl Slale Sept....ber lIIi. les7.1 LEGISU ilVE co1JNSE1. 'S DICEST' SB 531, Campbell. State rll'e Marshal: violations of statutes relating to fire protection: apprenticeship program. 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C cCC~J5"''''~ = 5 51l1l..c~e" .s o.c - oc:a.=:c .~ ~ l5.j'~ ~ ; ~ '505 g~ e.:;-sii.g i ~'5 ~:a .g.g ~~ ~ i'~ r~ ~ ~ ~"61 j~i~ a]f; , ~~ !~i !i11 i il -!.8iil~ !l~j ~i ;i'~ i ~ a J !! 1J j ~ 1 .t- ~.:; -! ~ ~ ci 8 = Jj .. i ~ ~ · .t-~ ~ J Cl Clo s ~ 0 .t- J -: -! ! 'i ~, ~ ~ i Jig I {! ~ i ~ J j ~ is, - i ~ f ~ 'Q i f i f i l) ~ J t t e~~.;.c=~ ~'. ~ f~~;..~ si ~ ~! .50; ;~Q.=ij 8 1:8 ~~~ 8'i-! WI ~ .c.-Cl" ,;8,Cl':; !l;S~Cl" ::-,,';1 ~c~,"OllQ~ 8..!:!!ClC>Il-!l i' .!l ~ .5;e 5 ~ e J5::: iii 5 ~ ol: ~ >. a WI, 2 5 " t'i ~:; ol:':;~. = cIS 'i..s 'i iiQ,~ J5 -! ~:c F= ii .. e;>>::Clo'" e'" .t-Cl..Q lIQC"Cc:" g.t-.5 j...> > '"ii-" S i~i~~~J~li..2~~S=ifi~~~1~~~;~Sc~~gl~~4~!li~ Q,-5 ~-8i= i'5 ~ .ol: 8'5"5.6 S"'ol:~.! g 8i 8~~ i'~ i'a05.. .2 . . , -~~~~~~=~~=~~~~~~~~~~~~~~~~~~~~~~~~~~~~* . ,e \ APPENDIX C REGIONAL PLANNING DOCUMENTS I) Fair Sharc Principles 2) Fair Sharc Formula and Rcgional Action Plu 3) Joint Powcrs Agrccmcnt e e . e e e . . FAIR SHARE PRINCIPLES The rollowing inrormation represents the rair share principles adopted by the Southern Calirornia Hazardous Waste Management Authority. A rair share table based on the principles and rormula also rollows. This table will change periodically based upon changes in the data used in the rair share formula. Thus, the fair share table i~ inc:luded for inrormatiDftal DUrDose~ only. I. Every county and city in the region will accept responsibility ror the management or hazardous wastes in an amount proportionate to the hazardous wastes generated in the county and city. 2. E.ach county shall meet its obligation in managing hazardous wastes either by siting racilities to treat and dispose or hazardous waste or by entering into intergovernmental agreements with other counties to site racilities. 3. The Authority encourages the siting or treatment racilities in counties where there is a substantial un met need ror the type or treatment which a racility would provide. The Authority . will consider the relative risk or wzste types and treatment methodology in the rair share allocation or racilities. 4. The minimum rair share responsibility ror each county shall be to have some combination or racilities sited within the county, lIUI. intergovernmental agreements with other counties - which will equal the county's orr -site hazardous waste generation. 5. The maximum rair share responsibility ror each county will be to have racilities sited within the County that equal the orr. site waste generation or the county. A coun,ry may choose to site racilities in excess or that county's orr -site waste generation. 6. The Authority will assist and support local government siting or racilities consistent with the rirst rive rair share principles through the regional action plan. The Authority will support local governments in their local land use decisions which are consistent with the rair share principles. 7. Fair share determination is dynamic and will change based on economic growth, progress in waste minimization, technological ad'vancement, and progress in siting new racilities. The rair share determination ror each county shall be made annually by the Authority based on the most recent generation data aDd projections, and whenever a new racility is sited or an existing one expanded or restricted. C.l . . FAIR SHAR.:E FORMULA - " A. Regional unmet needs equals regional waste generation less existing regional waste treatment capacity (for cach trcatment category). B. Fair share allocation of regional unmet need equals regional unmet needs by treatment category. allocated proportionately among counties that generate more off-site wastes than they treat. divided by facility size assumptions. REGIONAL ACTION PLAN The fOllowing elements of the Southern California Hazardous Waste Management Plan Action Plan should be considered for use when facility siting proposals-are being reviewed and acted on by a local government in San Bernardino County. o Authoritv Technical A~sistanee to LOCBI Jurisdiction~. The Authority can assist local governments in identifying inter jurisdictional issues related to the siting of facilities. and the implemen tation of measures to address these issues based on the Southern California Plan. o Model Inter~overnmental A2reements developed by the Authority to document interjurisdictional transfers of hazardous waste for purpose of fair- share monitoring and implementation. e o Other A uthoritv Prollrams _ with the potential to assist local governments in facility siting reviews and decisions are a liability insurancc program for local governments and a program to develop financial incentives for these jurisdictions. e .'i C.2 . . e ] - ~ ... 0 =: .. .. .. .. - e .,; .;. .;. N .. .. ..; ,: : ;;\'" .. .. .. . - - .=0 0" .. 0: II 0 - .. .. .. . :: .. .. .,; .. ..; .,; .,; .,; .,; ..; ..l - ;; ~~ :ii.. 0 "': .. - - - 0 - "! . . . .,; .,; .,; .,; .,; .,; .; .. ..l - - 0: 0 0: .I~ .. . . 0 "': .. . "; 0 0 - - E .,; - .,; .,; .,; ~ .,; N .: .'" . - = . :0 . ~13 0 - - - - ... 0 ~ "'! .,; .,; .,; .,; .,; .,; .,; .,; NO .~~ 0 0 ... .. 0 .. . - C: '" .,; .; .,; .,; .,; .,; .. .,; ., '" - E . " - ... . ..J S ~ ~ D 0: . 0 .. ~ ~ 0 - :: ~ - < j, .. ... .,; .,; .,; .,; . ... 0 on ~ .. ..", , f 0 0:% .. _E C <=8 .'" > =.. - e %00 ....0=0 i""":' ~I ~ ~ -"," 0 ..J~"' \I:-e-- C "'- 0:", l"'I 0 ..% ;; U '" 0 ": ~ ., ., .. - ... ... ~c .,; .,; .,; .,; D ..; 0: - - - - - 0 < co'" . - o . _ l :;; .!:, e c o co '" ! 0: "'0:- 0 ... ~ - - - 0 .. ., < . .,; .,; .,; .,; .,; .,; .,; .,; . - .. ... ..l . . I~ ~ - - ., - .. ... co - .. ;; . .,; ..; - .,; .,; .,; .,; .,; .. ... i ~ - .. ., .. .. - 0 - E 0 ~ .. 0 - 0 ~ ... . _ll C N .,; .,; .,; .,; 0 ..; . ..l, . 0 .. ] .. ~ "! 0 on ~ 0"; 0 ": ~ "0 . e .,; - .,; .,; 0 0 .,; .,; ..; CO ~ "'loI'.l 0" C .. .. o = ~ ';10 . 0 O':J 0 .:.. < II 0 - - "! "l 0 "l "l .. . .. ..l .,; .,; .,; 0 0 .,; 0 0 .,; -~ - l" ;; "l -, .. . ..f 0 o _ . .. '" ..... o C .. 0- ~ . 0 .. .. . 0 0' 15 0 "a < II 0 .,; .- .. ... .- I -- .. -- e .. . II .. :r: .. II .. I.l_ ;; .. . II . .. c . % := r :! - .. .. .. - . ~ .. . .. Q . 0 .. .. - < r - .. .. 6 ...... .. .. i i .: ... . .. . c c ... ! oS - iii .. .. . .. . . 0 '" III III ~ 0: "'- . . . Southern California Hazardous Waste Hanagement Authority Agreement e j JOINT EXERCISE OF POWERS AGREEMENT FOR HAZARDOUS WASTE ~AHAGEMENT ~ . WITNESSETH: This Agreement is entered into under the provisions of Article I of Chapter 5, Division 7, Title "1 of the Government Code, concerning joint powers agreements. Local governments in Southern California desire to work together to establish and implement an equitable allocation of hazardous waste management facilities called for in the regional Action Program developed by ~he Southern California Hazardous Waste Management Project. . NDW, THEREFORE, THE JURISDICTIONS AG~EE AS FOLLOWS: 1. 'OBJECTIVE The purpose of this Agreement is to create a joint city-county Hazardous Waste Management Authority responsible for coordinating the implementation of the Southern. California Hazardous Waste Management Action Program. For ~. the protection of the public health and welfare, the Authority will seek ,.., the implementation of the Action Program through the appropriate city and. county processes to ensure the Development of programs and the siting of facilities sufficient to safely manage hazardous wastes generated within Southern California. Actual siting decisions will continue to be vested in iocal sover~~:r.ts, through the exercise of their existing land .use e~th~rity. 2. DEFINITJOHS Certain words as used in this Agreement shal' be defined as follows: , . a. "Action Program. shall mean those undertakings and responsibilities as specified in Section 6 of this Agreement. b. "Board. shall mean the board constituted herein pursuant to this ~9reement to administer and" execute this Agreement. c. "Councils of Governments. shall" mean the Southern California ~ssociation of Governments. the San Diego Association of Governments, and the Santa Barbara County-Cities Area Planning Council. d. "Hazardous Waste Management Authority" shall mean the public and separate agency created by this Agreement. e. "Jurisdiction" sha" mean each City or County which is a signatory to this Agreement. - C~ e ,e , e . . f. "Region. ~hall mean the countie~ of-Imperial, Los Angeles, Orange, Riverside, San Bernardino, San Diego, Santa Barbara and Ventura, and the cities within these counties, together with any other public entity that may execute this Agreement in the future. 3. EffECTIVE DATE This agreement shall become effective immediately after four or more counties have executed this Agreement. 01. CREATION Of AUTHORITY. . There is hereby ereated a Hazardous Waste Management Authority (hereinafter referred to as "Authority.) to exercise in the manner hereinafter set forth the powers common to each of the Jurisdictions. The Authority shall be a public entity separate from the Jurisdictions. No debt, liability, or obligation of the Authority shall constitute a debt, liability, or obligation of any Jurisdiction, and each party's obligation hereunder is expressly limited only to the appropriation and contribution of such funds as the parties hereto may agree to and direct in accordance with this Agreement. 5. POWERS The Authority shall have the following pO\o,'ers to implement the provisions of this Agreement and is hereby auth~rized in its Oft~ n~~e to perform all acts necessary for the exercise of said powers: a. to h.a!:e and enter into contracts; b. to apply for and accept grants, advances, and contributions frem any source including m!~~er Jurisdictions; c. to e~ploy or contract fer the services of agents, e~ployees, con- suitants and such other persons or firms as it deems necessary; d. to me!:e plans and conduct studies; e. to sue and be sued in its own name, except that in the event of a breach of this Agreement, the Authority shall not sue any Jurisdictien nor any e~ployee or agent of any Jurisdiction thereof; f. to incur debts, liabilities, or obligations, subject to the limitations herein set forth; g. to adopt annually a budget setting forth all administrative, o~!ra- tiAnal and capital expenses for the Authority, together with the apportion- ment of such expenses to each Jurisdiction; h. to serve as an advocate before state and federal permitting authorities in support of applications to establish any hazardous waste treatment facility which has the approval of the local juriSdiction in which the facility would be located, in accordance with the objectives of the Action Program; c.s . . i. to provide financial assistance to member Jurisdictions to defray costs of participation in this.Agreement; j. to sponsor p~grams to aid the implementation of the Action Program. These powers shall be exercised in the 'manner that such powers are regularly exercised by Riverside County. 6. ACT10H PROGRAM . The following actions reference the Southern California Hazardous Waste . Hanagement Project's fina' teChnical findings as reported in The Problems and Heeds for the Adequate Kanaoement of Hazardous Wastes in Southern California and the Sitino Kanual. Each action should be implemented through the appropriate county or city agency within a one-year time frame. The Action Program herein is based upon the "fair share" concept that every city and county in the region will accept responsibility for the rnena;ement of h02ardous wastes in an amount proportional to the hazardous wastes generated within the city or county. Progress shall be reviewed quarterly by the Hazardous Waste Kenaoement Soard. a. Each Jurisdiction shal' adopt for 'oca' use the Project's siting criteria contained in the Sitino Hanual in evaluating any proposal for a hazardous waste' facility including those submitted prior to January 31, . 1985. nothing in the Joint Powers Agreement shall preclude any Jurisdiction from deve'o~ing, adopting, and using in such evaluations, in addition to the Project's siting criteria, its Oftn siting criteria based upon that Jurisdiction's unique, local conditions Dr concerns, so 'long as such local criteria are compatible with the adopted Project criteria. b. Each Jurisdiction should 'develop a program to encourage onsite source reduction, recycling, and treatment. c. Each Jurisdiction should examine and act on the collection service needs of its industries and smal' generators who depend on offsite facilities and services. d. The ,Hazardous Waste E'ement of the solid waste manegement plan for eech Jurisdiction ~hall focus on the treatment, storage, and disposal requirements identified in the Project's final technical report on ~eeds assessment. e. Each Jurisdiction with specific types of treatable hazardous wastes which are currently sent offsite and are in large enough volume to justify a separate treatment facility should solicit proposals for the appropriate facilities as outlined in the Table attached. The facilities may provide single or multiple treatment options appropriate to that Jurisdiction's primary hazardous wastes. - C~ .e e e . . f. Each Jurisdiction whose currtnt offsite wastes do not justify the sma"est capacity faci'ity shou'd so'icit proposa's for the appropriate transfer stations, co"ection centers, or specialized collection services as depicted in the Table attached. g. Under the Tab'e attached, each Jurisdiction with wastes appropriate to a specific type of treatment techno'ogy sha1' give priority consideration to any proposa' submitted to it which includes a faci'ity using that techno'ogy. If a Jurisdiction with sma" vo'umes of hazardous wastes agrees to site a faci'ity, it wi" be compensated by other Jurisdictions making use of the faci'ity. The terms of compensation should be determined according to guide1ines approved by the Hazardous Waste Poa~asernent Board. h. Each Jurisdiction sha'l submit a quarter'y and annua' progress report to the Hazardous Waste Hanagement Board. i. This Action Program may be amended on'y by a two-thirds (2/3) vote of the members of the Hazardous Waste Poanagement Board, such ~"endments to be effective si~ months after adoption. 7. ORGAHIZATIOH a. Hazardous Waste H~~aoement Beard The Authority sha" be ooverned by the Ha.ardous Waste Hanaoernent Soard which shal' exercise a" powers and authority on beha'f of the Authority. The E.~ard is e...;:o~er::d to estab'ish its own I'rocedures. The Seard r;',ay eo any and a" thIngs ~~cessary to carry ,ut the purposes of this Agreement. The ;oard sha" consist of: i. One member of the governing body of each county signing this A.oreem;.Tit; ii. A representative of the City of Los Ange'es; iii. A representative of the City of San Diego; and. iv. One person representing a" of t~e cities in each county. Upon execution of this Agreement, the governing body of each county, the. City of Los Ange'es and the City of San Diego sha" appoint one of its members to serve as a member of the Board and another elected official ....ithin the county/city to .serve as an a'ternate member of the iloard in the absence of the regular appointee. A Jurisdiction may request the Board to accept a nonelected officia' as its voting alternate on a sing'e meeting basis. Such request sha'l not be unreasonab'y denied. The Counci's of Gover~"ents sha1l each appoint a representative and an a'ternate for the cities in each of their counties, in accordance with the city selection process, determined within each county. By unanimous agreement, the Board may e~pand its membership. C., . . each member and alternate ~hall hold office from the fir~t meeting of the Board after his appointment until a successor is selected. Each member and alternate shall serve at the pleasure of the Appointing Jurisdiction or Council. e " b. Councils of Governments The Chairpersons of the three Councils of Governments within the region, namely the Southern California As~ociatieri of Governments (SC~G), the San Diego Association of Governments (SANDAG), and the Santa Barbara County--Cities. Area Planning Council, ~hall serve as ex officio nonvoting members of the Beard.' After this Agreement becomes effective, the governing body of each council of governments shall also appoint one of its members to serve as an alternate ex officio nonvoting member of the Beard to ~erve in the absence of the Chairperson. The Councils of Governments shall not become signatories to this Agreement. . c. Vote Reouired . " A rr.~jority vote of those Soard r.,em~ers present and voting shall be required for ~ny action except as otherwise provided herein. The Board shall adopt through its byle~s or other means, a voting procedure which would per~it city or county re~resentetives upon reques~ to require a majority of both city and county representatives present to affir;,atively adopt an action before the Beard, . d. ~:=Et i r,os of the Soard , e (1) ~eoular Heetinos The B~~rd shall hold at least one regular meEting each year. The date upon ~hichi and the hour and place at which each such re~ular meeting shall be held shall ~e fixed by resolution of the Soard. (2) Soecial Meetinos , . Special maetin;s of the Board may be called in accordance with the provisions of Section S~95S of the' California Gover~~ent Code. (3) ~otice of ~ee:1nos All meetings of the Board ~hall be held subject to the provi~ions of the Ralph M. Broom Act, being Sections SQ9SO et ~eq. of the California Gover~~ent Code, and ot~er applicable laws of the State of California requiring notice of mee:ings of public bodies to be given. Notice shall also be given to any party requesting such notice in writing. (4) Minutes The Board shall cause minutes of all meetings to be kept and shall, ~ as soon as pos~ible after each meeting, cause a copy of the minutes to be ~ fo~'arded to each member of the Board and to eech Jurisdiction. - C-ll . . e (5) Ouon::l\ A ~ajority of the voting m~mbers of the Board sha" constitute a ~uorum for the transaction of business, except that less than a ~uorum ~ey adjourn fro:l\ time to time. e. By) e\<'s The Soard shall adopt from time tD time such bylews, rules or , regulations for the conduct of its affairs es may be re~uired. B. ST AFf'l NG The Soard ro.ey re~uest SeAG, SASOAG, end the Stnt! Eubare Count)'--Cities ~,rH Planning Council or melr.ber Jurisdictions to provide staff support to the Beard as ~ey be necessary for the Board to fulfill its duties. The ;card ~ey elso hire such staff as mey be necessary to accomplish its purpcses. O -1.'....,. ~I'" ... ~\!:..L:.: L';:,cn s':;niI'l9 this ;'.;ree;;.ent, each county, the City of Los Angeles, and the City of $en Oi~go shell cc~trlbute a fee of Ten Thousand Dollers ($10,OOD) :0 f~~~ th! cctivities of the Authori:y. ,0. r,":~S. AUDIT ~~D ACCOU~TING SERVICES e r~-~:.:e.,t to tr.e re!:!uiremer.ts of Stction (505.5 of tr.: !::.ern::-.ent Code, the '7-:et:.:r;;r of ~herdce COl.inty is hereby desigr.<t~d to :! ',he depo.sitory er,d :0 r,,"e cu~tc.dy of ell Authority f.mos frc::! Ior,et!\Qr so:;rce, p,nd to perfer::! t~! fo'io~1n; f~nct~~nt: e. Receive end receipt fer all moneys for.the ~~thority end pi!ce It in the desigoetfd perty's Treesury for the credit of the A~therity; b. ~e responsibie upon official bond for the safekeeping end c~sbursement of ell Authority mcney so heid; c. Pey any sum due from the Authority from Authority money, or a.,y ;,:"~;cn t:,ereof, tonly upon ...arnnts of the publiC pfficer perfor.;;ing the f~~::;ons of Auditor who has been so designated by this Agreement; and d. Verify end report in ~Titin9 on the first cey of July, October, :an~ery, and April of each yeer to the Soard end to the contracting perties to this A;ree~ent the emount of money the Treasurer hoids for the Aut"cr1ty, the ~cunt of receipts and the amount paid out since the last rcrort to the Board. The functions of Auditor shel' be performed for the Authority by the Aucitor/Controller of Riverside County. The Auditor shall drew warrants to ~ey demands egainst the Authority when the demands have been approved by the Board or by a person authorized by the Board tD so approve. e There shall be strict accountability of al' funds and the Auditor wil' C-9 . . r!port to th! Stat! Board of Control all r!c!ipts and disbun!l:lent$. In _ addition, the Board will direct the Auditor to make or it will contract for ~ an audit of the accounts and records at least annually as prescribed by Section 6505 of the Government Code. In either case the minimum requirements of the audit shall be those prescribed by the State Controller for special districts under Section 26909 of the Government Code and the audit shall conform to generally accepted auditing standards. 11. ' DISPOSITION OF AUTHORITY FUNDS UPON TERMINATION ' Authority funds, including any interest Earned on deposits, rema1n1ng upon termination of the Hazardous Waste Management Authority after payment of all' obligations, shall be returned in proportion to the contribution of each Jurisdiction during the term of this Agreement. ,Decisions of the Board shall be final in this regard. 12. WITHDRAWAL Any Jurisdiction upon six months written notice given to the Haz~rdous ~~ste ~ancgement Board may withdraw from this Agreement. Such withdra.al shall not affect any obligations of the Jurisdiction incurred before the effective date of the w1thdrawal. 13. .eJo\ENDKEIiTS, This Agree~ent ~~y only be ~nded ~ith the consent of a'l ~~rt;es ~h;ch _. ~r! sisnatories to this Agreement. ~ , 1~. NOTI CES " Al' notices to Jurisdictions sha" be deemed to have been oiven ~hen ~eiied to the legis1ativebody of each Jurisdiction. Notices.to the Authority she" . be sent to the Htzardous ~este ~aneoer.,ent Beard at an address to be officially established by the Board. . Notices to the Councils of Governments shal' be sent to their Executive Directors. e C-IO e ,e \- 'e . . III WITNESS WHEREOF," each JURISDICTIOII has executed approval of this Agreement. ~ It? ~,<,....~ ~ ha~rperson, Board of Supervisors, '5 August 12, 1985 Date San Bernardino County Date Haj'or. City of C-Il ,e ,e e . . APPENDIX D W Am CODES. W Am GROUPS AND GENERALIZED TREATMENT METHODS. J ) WASTE GROUPS LISTED BY CALIFORNIA WASTE CATEGORIES 2) CONVERSION OF CALIFORNIA WASTE CATEGORIES TO WASTE GROUPS 3) GENERALIZED TREATMENT METHODS FOR EACH W Am GROUP .Sourec: Califorllia Departmcat of Health Services, Altcrnativc Techllology Section, Guidelines for the Premlnttion Dr HazardoD! WaIte Mallal!emeDt flG. Tcchaical Rcfercllcc Maaaal, 1986. . . ,e '1'ULZ ])-1 nSTE GIlOtrPS L1:S'1'!:D IIY C~L1:JI'OIlN1:A nSTE C~'1'EGOIl1:ES WASTE GROUP CALrJl'OIlN1:A nSTE C~'1'!:GOIlY WASTE OIL 221 WASTE OIL AND MIXED OIL 223 UNSPECIFIED OIL CONTAINING WASTE HALOGENATED SOLVENTS 221 HALOGENATED SOLVENTS 741 LIQUIDS WITH HALOGEN .ORG. COMPo > 1000 MG/L NON-HALOGENATED SOLVENTS 212 OXYGENATED SOLVENTS 2 13 HYDROCARBON SOLVENTS 214 UNSPECIFIED SOLVENT MIXTURES 4itRGANIC LIQUIDS 133 AQUEOUS WITH TOTAL ORGANIC > 10% 134 AQUEOUS WITH TOTAL ORGANIC < 10% 3U 0 R G A N I C ( NON SOL V E N T S ) LIQUIDS WITH HALOGENS 342 ORGANIC LIQUIDS WITH KETAL 343 UNSPECIFIED ORGANIC LIQUID MIXTURES PESTICIDES 231 PESTICIDE RINSE WATER 232 PESTICIDE AND PESTICIDE PRODUCTION & WASTE PCBs DIOXINS 261 POLYCHLORINATED BIPHENYLS 731 LIQUIDS WITH PCBs > 50 MG 801 WASTE POTENTIALLY CONTAINING DIOXINS OILY SLUDGES 222 OIL/WATER SEPARATION SLUDGE 352 OTHER ORGANIC SOLIDS 481 TETRAETHYL LEAD SLUDGE e 0-1 . . HALOGENATED ORGANIC SLUDGES & SOLIDS 251 STILL BOTTOMS WITH HALOGENATED e ORGANICS 351 ORGANIC SOLIDS WITH HALOGENS 451 DEGREASING SLUDGE 751 SOLIDS WITH HALOGEN. ORG. COMPo > 1000 MG/KG NON-HALOGENATED ORGANIC 241 TANK BOTTOM WASTE SLUDGES & SOLIDS 252 OTHER STILL BOTTOM WASTE 321 SEWAGE SLUDGE 471 PAPER SLUDGE/PULP 491 UNSPECIFIED SLUDGE WASTE 571 FLY ASH I BOTTOM ASH AND RETORT ASH DYE & PAINT SLUDGES & RESINS 271 ORGANIC MONOMER WASTE 272 POLYMERIC RESIN WASTE 281 ADHESIVES 291 LATEX WASTE 461 PAINT SLUDGE METAL-CONTAINING LIQUIDS III ACIDS WITH METALS 121 ALKALINE: WITH METALS 132 AQUEOUS WITH METALS e METAL-CONTAINING SLUDGES 171 METAL SLUDGE METAL-CONTAINING LIQUIDS 721 LIQUIDS WITH ARSENIC > 500 MG/L 722 LIQUIDS WITH CADMIUM > 100 MG/L 723 LIQUIDS WITH CHROMIUM> 500 MG/L 724 LIQUIDS WITH LEAD > 500 MG/L 725 LIQUIDS WITH MERCURY > 20 MG/L 726 LIQUIDS WITH NICKEL > 134 MG/L 727 LIQUIDS WITH SELENIUM> 100 MG/L 728 LIQUIDS WITH THALLIUM > 130 MG/L e 0-2 r . _ANIDE & METAL LIQUIDS I.. NON-METALLIC INORGANIC LIQUIDS NON-METALLIC INORGANIC SLUDGES .SOIL XISCELLANEOUS WASTES e e . 711 LIQUIDS. WITH CYANIDES > 1000 MG/L 112 ACID WITHOUT METALS 113 UNSPECIFIED ACID 122 ALKALINE WITHOUT METALS 123 UNSPECIFIED ALKALINE 131 AQUEOUS WITH REACTIVE ANIONS 135 UNSPECIFIED AQUEOUS SOLUTION 791 LIQUIDS WITH Ph < 2 411 421 431 441 521 611 141 151 161 162 172 181 .311 322 331 511 512 513 531 541 551 561 581 591 612 ALUM AND GYPSUM SWDGE LIME SWDGE PHOSPHATE SWDGE SULFUR SLUDGE DRILLING MUD CONTAMINATED CONTAMINATED SOIL OFF-SPEC, AGED OR SURPLUS INORGANICS ASBESTOS-CONTAINING WASTE FLUID CATALYTIC CRACKER WAS'l'E OTHER SPENT CATALYST METAL DUST OTHER INORGANIC SOLID WASTE PHARMACEUTICAL WAS'l'E BIOLOGICAL WASTE OTHER THAN SEWAGE SLUDGE OFF-SPEC, AGED OR SURPLUS ORGANICS EMPTY PESTICIDE CONTAINERS > 30 GAL OTHER EMPTY CONTAINERS > 30 GAL EMPTY CONTAINERS < 30 GAL CHEMICAL TOILET WASTE PHOTOCHEMICALS/ PHOTOPROSESSING WAS'l'E LABORATORY WAS'l'E CHEMICALS DETERGENT AND SOAP GAS SCRUBBER WASTE BAGHOUSE WASTE HOUSEHOLD WASTES D-3 . . n.BLZ D- Z e OONVERBYOH OP eALYPORHY~ W1BTE e1~BORY2B ~O ~STB GROUPS CAL:tlPOJUcrA nS'l'B CA'!'EGORY 111 112 113 121 122 123 131 132 133 134 135 141 151 161 162 171 172 181 211 212 213 214 221 222 223 231 232 241 251 252 261 271 272 281 291 ACIDS WITH METALS ACID WITHOUT METALS UNSPECIFIED ACID ALKALINE WITH METALS ALKALINE WITHOUT METALS UNSPECIFIED ALKALINE AQUEOUS WITH REACTIVE ANIONS AQUEOUS WITH METALS AQUEOUS WITH TOTAL ORGANICS >lot AQUEOUS WITH TOTAL ORGANICS <lot UNSPECIFIED AQUEOUS SOLUTION OFF-SPEC, AGED OR SURPLUS ORGANICS ASBESTOS-CONTAINING WASTE FLUID CATALYIC CRACKER WASTE OTHER SPENT CATALYST METAL SLUDGE METAL DUST OTHER INORGANIC SOLID WASTE HALOGENATED SOLVENTS OXYGENA~D SOLVENTS HYDROCARBON SOLVENTS UNSPECIFIED SOLVENT MIXTURES WASTE OIL AND MIXED OIL OIL/WATER SEPARATION SLUDGE UNSPECIFIED OIL CONTAINING WASTE PESTICIDE RINSE WATER PESTICIDES AND PESTICIDE PRODUCTION WASTE TANK BOTTOM WASTE STILL BOTTOMS WITH HALOGENATED ORGANICS OTHER STILL BOTTOM WASTE POLYCHLORINATED BIPHENYLS ORGANIC MONOMER WASTE POLYMERIC RESIN WASTE ADHESIVES LATEX WASTE nB'!'E GROUP METAL-CONTAINING LIQUIDS NON-METALLIC INORGANIC LIQUIDS NON-METALLIC INORGANIC LIQUIDS METAL-CONTAINING LIQUIDS NON-METALLIC INORGANIC LIQUIDS NON-METALLIC INORGANIC LIQUIDS NON-METALLIC INORGANIC LIQUIDS METAL-CONTAINING LIQUIDS ORGANIC LIQUIDS ORGANIC LIQUIDS NON-METALLIC INORGANIC LIQUIDS MISCELLANEOUS WASTES INORGANICS MISCELLANEOUS WASTES MISCELLANEOUS WASTES MISCELLANEOUS WASTES METAL-CONTAINING SLUDGES MISCELLANEOUS WASTES MISCELLANEOUS WASTES HALOGENATED SOLVENTS NON-HALOGENATED SOLVENTS NON-HALOGENATED SOLVENTS NON-HALOGENATED. SOLVENTS WASTE OIL OILY SLUDGES WASTE OIL e PESTICIDES PESTICIDES NON-HALOGENATED ORGANIC SLUDGES it SOLIDS HALOGENATED ORGANIC SLUDGES it SOLIDS NON-HALOGENATED ORGANIC SLUDGES it SOLIDS PCBs it DIOXINS DYE it PAINT SLUDGES , RESINS DYE , PAINT SLUDGES , RESINS DYE , PAINT SLUDGES , RESINS DYE it PAINT SLUDGES it RESINS e D-4 ,_i " , \'~ 322 331 341 342 343 351 352 411 421 431 441 451 461 471 481 491 _11 512 513 521 531 541 551 561 571 581 591 611 612 711 721 722 723 ,e ". . PHARMACEUTICAL WASTE SEWAGE SLUDGE BIOLOGICAL WASTE OTHER THAN SEWAGE SLUDGE OFF-SPEC, AGED OR SURPLUS ORGANICS ORGANIC (NONSOLVENTS) LIQUIDS WITH HALOGENS ORGANIC LIQUIDS WITH. METALS UNSPECIFIED ORGANIC LIQUID MIXTURES ORGANIC SOLIDS WITH HALOGENS OTHER ORGANIC SOLIDS ALUM AND GYPSUM SLUDGE LIME SLUDGE PHOSPHATE SLUDGE SULFUR SLUDGE DEGREASING SLUDGE PAINT SLUDGE PAPER SLUDGE/PULP TETRAETHYL LEAD SLUDGE UNSPECIFIED SLUDGE WASTE EMPTY PESTICIDE CONTAINERS > 30 GAL OTHER EMPTY CONTAINERS > 30 GAL EMPTY CONTAINERS < 30 GAL -DRILLING MUD CHEMICAL TOILET WASTE PHOTOCHEMICALS/ PHOTOPROCESSING WASTE LABORATORY WASTE CHEMICALS DETERGENT AND SOAP FLY ASH I BOTTOM ASH AND RETORT ASH GAS SCRUBBER WASTE BAGHOUSE WASTE CONTAMINATED SOIL HOUSEHOLD WASTES LIQUIDS WITH CYANIDES > 1000 MG/L LIQUIDS WITH ARSENIC > 500 MG/L LIQUIDS WITH CADMIUM > 100 MG/L LIQUIDS WITH CHROMIUM > 500 MG/L . MISCELLANEOUS WASTES NON-HALOGENATED ORGANIC SLUDGES " SOLIDS MISCELLANEOUS WASTES MISCELLANEOUS WASTES ORGANIC LIQUIDS ORGANIC LIQUIDS ORGANIC LIQUIDS HALOGENATED ORGANIC SLUDGES " SOLIDS OILY SLUDGES NON-METALLIC INORGANIC SLUDGES NON-METALLIC INORGANIC SLUDGES NON-METALLIC INORGANIC SLUDGES NON-METALLIC INORGANIC SLUDGES HALOGENATED ORGANIC SLUDGES " SOLIDS DYE " PAINT SLUDGES " RESINS NON-HALOGENATED ORGANIC SLUDGES " SOLIDS OILY SLUDGES NON-HALOGENATED ORGANIC SLUDGES " SOLIDS MISCELLANEOUS WASTES MISCELLANEOUS WASTES MISCELLANEOUS WASTES NON-METALLIC INORGANIC SLUDGES MISCELLANEOUS WASTES MISCELLANEOUS WASTES MISCELLANEOUS WASTES MISCELLANEOUS WASTES NON-HALOGENATED ORGANIC SLUDGES AND SOLIDS MISCELLANEOUS WASTES MISCELLANEOUS WASTES CONTAMINATED SOIL MISCELLANEOUS WASTES CYANIDE " METAL LIQUIDS METAL-CONTAINING LIQUIDS METAL-CONTAINING LIQUIDS METAL-CONTAINING LIQUIDS 0-5 724 725 726 727 728 731 741 751 791 801 . LIQUIDS WITH LEAD > 500 MG/L . LIQUIDS WITH MERCURY > 20 MG/L LIQUIDS WITH NICKEL > 134 MG/L LIQUIDS WITH SELENIUM > 100 MG/L LIQUIDS WITH THALLIUM > 130 MG/L LIQUIDS WITH PCBs . > 50 MG/L LIQUIDS WITH HALOGEN. ORG. COMPo > 1000 MG/L SOLIDS WITH HALOGEN. ORG. COMPo > 1000 MG/XG LIQUIDS WITH Ph< 2 WASTE POTENTIALLY CONTAINING DIOXINS . METAL-CONTAINING LIQUIDS METAL-CONTAINING LIQUIDS METAL-CONTAINING LIQUIDS METAL-CONTAINING LIQUIDS METAL-CONTAINING LIQUIDS PCBs , DIOXINS HALOGENATED SOLVENTS HALOGENATED ORGANIC SLUDGES , SOLIDS NON-METALLIC INORGANIC LIQUIDS PCBs , DIOXINS 0-6 e )' e e e . . TAllIoE J)- 3 GEHER1L!:ZED '1'R.E1'1'MENT ~nODS POR B>>'CH W1Sl!'!: GROUP WASTE GROUP WASTE OIL HALOGENATED SOLVENTS NON-HALOGENATED SOLVENTS ORGANIC LIQUIDS PESTICIDES PCBs & DIOXINS OILY SLUDGES HALOGENATED ORGANIC SLUDGES & SOLIDS NON-HALOGENATED ORGANIC SLUDGES & SOLIDS DYE & PAINT SLUDGES & RESINS METAL-CONTAINING LIQUIDS _ANIDE & METAL LIQUIDS NON-METALLIC INORGANIC LIQUIDS METAL CONTAINING SLUDGES NON-METALLIC ::NORGANIC SLUDGES CONTAMINATED SOIL EMPTY CONTAINERS OFF-SPEC, AGED OR SURPLUS INORGANICS ASBESTOS-CONTAINING WASTE FCC WASTE OTHER SPENT CATALYST METAL DUST OTHER INORGANIC SOLID WASTE PHARMACEUTICAL WASTE BIOLOGICAL WASTE OTHER THAT SEWAGE SLUDGE OFF-SPEC, AGED OR SURPLUS ORGANICS e PRlJO.RY TREATMENT HETROD ALTERnTrv!: '1'R!:ATKER'.!' HETROD OIL RECOVERY SOLVENT RECOVERY SOLVENT RECOVERY OTHER RECYCLING AQUEOUS TREATMENT ORGANIC INCINERATION OIL RECOVERY INCINERATION INCINERATION INCINERATION INCINERATION AQUEOUS ORGANIC TREATMENT OTHER RECYCLING INCINERATION SOLVENT RECOVERY INCINERATION SOLVENT RECOVERY OTHER RECYCLING OTHER RECYCLING INCINERATION AQUEOUS TREATMENT METALS/NEUTRALIZATION AQUEOUS TREATMENT METALS/NEUTRALIZATION AQUEOOS TREATMENT METALS/NEUTRALIZATION . STABILIZATION STABILIZATION INCINERATION OTHER RECYCLING STABILIZATION OTHER RECYCLING OTHER RECYCLING OTHER RECYCLING OTHER RECYCLING OTHER RECYCLING STABILIZATION STABILIZATION STABILIZATION OTHER RECYCLING OTHER RECYCLING OTHER RECYCLING OTHER RECYCLING STABILIZATION STABILIZATION AQUEOOS TREATMENT ORGANIC OTHER RECYCLING INCINERATION INCINERATION STABILIZATION D-7 WAS'rE GROUP CHEMICAL TOILET WASTE PHOTOCHEMICALS/PHOTO PROCESSING WASTE IABORATORY WASTE CHEMI CALS DETERGENT AND SOAP GAS SCRUBBER WASTE BAGHOUSE WASTE HOUSEHOLD WASTES . PRI:KAll.Y '1'REA'l'MEN'r lm'!'Ron STABILIZATION OTHER RECYCLING OTHER RECYCLING OTHER RECYCLING AQUEOUS TREATMENT METALS/NEU'l'RALIZATION STABILIZATION OTHER RECYCLING D-8 . J..L'1'!:R!D. 'l'rv!: '1'REA'l'MEN'r HEROn STABILIZATION STABILIZATION STABILIZATION STABILIZATION STABILIZATION - j - - . . . APPENDIX E 1USTIFICA TlON FOR THE SAN BERNARDINO COUNTY SmNG CRITERIA . . e e e . . JUSut;lCATION FOR. CHANGES TO THE SITING CR.ITER..lA The purpose of this appendix is to justify changes from the Department of Health Services (DHS) criteria. Each of the recommended County criteria is presented with a short explanation of the changes made to the DHS criteria. The Guidelines for preparing Hazardous Waste Management Plans prepared by the DHS specify that the criteria presented therein be- used in the County Plan. The Guidelines also sute that "If the CHWMP authors desire to take exception to any of the criteria, they shall discuss reasons for doing so in the draft submitted for comment to the Department." The criteria presented in the County Hazardous Waste Management Plan (CHWMP) were developed from the DHS criteria. The issues and concerns found in the DHS criteria are all addressed in the County of San Bernardino Plan either as siting criteria or policy statements. The language of the criteria was modified to incorporate the specific concerns of the County based on comments received from the CHWMP Advisory Committee, members of the public, and local jurisdictions and agencies. The criteria recommended by the DHS for inclusion in CHWMP relating to the use of industrial, commercial, and specifically zoned lands and other state, federal, and Indian lands have been included as policy statements (P/A.S-4-(I) and P/A-S-12 respectively). 1. PR.OXIMITY TO RESIDENCES a. A 2000 foot buffer zone from residences shall be required for any land disDosal facilitv unless the owner demonstrates to the satisfaction of the County or city and the State Department of Health Services that a buffer zone of less than 2000 feet is adequate for the protection of public health and safety. To determine the appropriate buffer a risk assessment shall be required which considers the physical and chemical characteristies of the specific type of wastes that will be handled, the design features of the facility, and any need for buffering residential areas or other sensitive areas from potential accidents or adverse emissions from a proposed facility. b. A risk assessment shall be required for any -treatment recvclin2 stor8.Il!l~ and transfer racilities, The risk assessment should consider the physical and chemical characteristics of the specific type of wastes that will be handled, the design of the facility. and any need for buffering residential areas or other sensitive areas from potential accidents or adverse emissions from a proposed facility. E.I . . Justirication e Two minor changcs wcre made to the DHS criterion. Reference to considering potential accidents was added. The County believes that this issue must be includcd in ordcr to adcquatcly cvaluate possiblc risks to the population. Risk is dcrincd a 'a mcasure of the likclihood and thc scvcrity of injury' (Govcrnors Task Forcc on Toxics, Waste and Tcchnology, Final Rcport, Volumc 2, May 19S6, pagc 251). The sccond chanle involvcs the rcfcrcncc to thc County in establishins a buffcr of lcss than 2000 fcct in critcrion l(a). Thc County should be involvcd in dcsilDatins an appropriatc buffcr so that consistcncy with the Boals and policics of thc Gcncral Plan can bc asccrtaincd. County (or City) involvcmcnt in this issue is consistcnt with the police powcr grantcd by the California Constitution which establishcs the local govcrnmcnt role in protccting the public hcalth, safcty, and wclfare of its rcsidcnts. 2. PROXIMITY TO IMMOBILE POPULA nONS Sneeiried h2.~ardou~ waste facilities shall be sited so that DO significant risl:: is prcscntcd to the immobile population. An adcquate buffcr betwccn the hazardous waste facility and the immobile population shall be establishcd by a risk asscssmcnt. Thc risl:: asscssmcnt shall consider the physical and chemical characteristics of the specific types of wastes which will be handlcd and the design fcatures of the facility and' proximity to immobile populations. Immobile populations include schools, hospitals, convalesccnt homes, prison facilitics. facilities for the mentally ill, etc. e Justification The proposed criterion is consistent with the DHS criterion. 3. PROXIMITY TO PUBLIC FACILITIES Sneciried ha~&rdous wRste facilities should be sited in such. manner. as they do not adversely impact the public health and safety of larle numbers of people in public areas or people in public facilities. An adequate buffer shall be determined by a risk assessment. Justification The purpose and intent of the DHS criterion has not chansed. The DHS criterion refers to two separate issues; the necessary distance from public places and the need for onsite water, sewer and emergency response services (self-sufficient services). The DHS criterion has been separated into these two distinct issues: Proximity to Public Facilities and Provision of Public Services. e E.2 e e e . . ... PROVISION OF PUBLIC SERVICES Specified hazardous waste facilities should be located in areas where emergency response capabilities and public water and sewer services are available. When facilities arc located in desert or rural areas where public services are not readily available. privately-owned onsite water, sewer. and emergency services (self-sufficient services) ma y be used. J ustifica lion This criterion reflecu the intent of the DHS criterion. It rccommencls the availability of public services but docs not make it manclatory. The criterion allows for mitigating measures if llublic services are nOI available. The recommencled types of trained personncl and emergency equipment will clepend on the particular characteristics of each facility. (See also previous comment.) 5. FLOOD PLAIN AREAS a. Land disDosal facilities may not be located in areas subject to 10o-year events ~ with protection (CFR. Title "0, Section 264.18 (b) and CCR Title 22, see Section 66391 (a)(lI)(b)). Flood plain areas include areas subject to r100ding by dam or levee failure and natural eauses such as river r1ooding, rainfall or snowmelt, tsunamis, seiches and coastal r1ooding. b. Treatment. reevclinl! nora2e and tran!:reT' r.ci'Iities may be located in areas subject to 10o-year r100dinB if -designed. constructed, operated, and maintained to prevent failure due to such events. Flood plain areas include areas subject to r100ding by dam or levee failure and natural causes such as river r1ooding, rainfall or snowmelt. tsunamis. seiches and coastal r1ooding. J ustifica lion The proposed criterion is very similar to the one suggested in the guidelines. The only difference is that part (b) - of cri~erion uses the words 'designed. constructed, operated. and maintained'. These words are standard ones used in the CCR when describinB containment structures or mitigation measures (See CCR. Subchapter IS. Title 23. Section 2531 (c)). 6. PROXIMITY TO ACTIVE OR RECENTLY ACTIVE FAULTS No sDecified hazardous waste facilitv should be placed within 200 feet of an active or recently active fault. (California Code of Regulations. (CCR). Title 22. Section 66391 (a) (II) A (I) and (2). E-3 . . Justirication - ., , The OHS criterion is recommended with minimal word changes. 7. UNSTABLE SOILS a. Land disDosal facilities shall not be located in areas of potential rapid geologic change (Title 23. SubChapter IS. Section 2531 (e) of the CCR). b. Treatment reevelinR st0r82e. and trlln~rer facilities may be located in areas of potential rapid geologie change if designed. constructed. maintained. and operated to prevent failure as a result of such changes (Title 23. SubChapter IS. Section 2531 (e) of the CCR). Justirication The changes made to the OHS criterion were taken from information found in Subchapter IS. Title 23 of the California Code of Regulations (CCR), The CCR defines rapid geOlogic change as an .alteration of the ground surface through such actions as landslides. subsidence. and faulting,. Section 2531 (e) specifies that land disposal facilities .shall be located outside areas of potential rapid geologic change." The CCR does allow mitigation for other facilities. The proposed criterion differs from the one recommended by the OHS but is consistent with state law. e /' I. DEPTH TO GROUNDWATER a. Land disDosal facilities shall be located where natural geologic features provide a natural barrier that prevents contamination of vital groundwater resources by waste and leachate (Title 23. SubChapter IS. Section 2531 (a) of the CCR) and whic:h meet the siting requirements of the State Water Resources Control Board. b. Treatment reevelin2 stor82e and tran!fer facilities shall be located where natural geologie features prevent the contamination of groundwater unless the engineering design and construction of the facility and containment structures are capable of preventing signiricant adverse impacts to groundwater. J ustirica tion The CCR. Subchapter 15. Title 23. Section 2531 states that: .Class I disposal units shall be located where natural geOlogie features provide optimum conditions for isolation of wastes from waters of the state." e E-4 e e e . . The regulations go on to state that disposal facilities must be underlain by natural geologic materials "_.which are of sufficient thickness to prevent vertical movement of fluid, including waste and leachate_" (CCR, Section 2531 (b)( I n. Based on this information we added reference to the need for natural geologic features to prevent vertical movement of wastes. While this reference has been applied to all facilities, facilities other than land disposal facilities have the flexibility to mitigate any potential impacts to groundwater. The criterion allows for the siting of facilities . consist with state requirements. Requiring a natural barrier between the facility and groundwater resources allows for mitigation or correction of a problem before accidental contll1llination reaches the groundwater. 9. MAJOR RECHARGE AREAS FOR AQUIFERS a. Land disDosal facilities should be prohibited within any area known or suspected to be supplying principal recharge to a regional aquifer as defined in state, regional, or general plans. The County General Plan and Bulletin "118, 1975, of the California Department of Water Resources identify the fOllowing as regional aquifers: Ames Valley (7-16) Antelope Valley (6-44) Bear Valley (g-9) Bessemer Valley (7-15) Big Meadows Valley (g-7) Ca ves Canyon Valley (6-38) Copper Mountain Valley (7-11) Dale Valley (7-9) Deadman Valley (7-13) EI Mirage Valley (6-43) Harper Valley (6-47) HelendaleFault Valley (7-48) Iron Ridge Area (7-50) Johnson Valley (7-18) Kane Wash Area (6-89) Lavie Valley (7-14) Lost Horse Valley (7-51) Lower Mojave River Valley (6-40) Lucerne Valley (7-19) Means Valley (7-17) Middle Mojave River Valley (6-41) . Morongo Valley (7-20) Needles Valley (7-44) Pipes Canyon Fault Valley (7-49) Seven Oaks Valley (g-8) Troy Valley (6-39) Twentynine Palms Valley (7-10) Upper Mojav'e River Valley (6-42) Warren Valley (7-12) Upper Santa Ana Valley (g-2) E-S . . b. Treatment re~velin2 UorSRe and transfer facilities may be located in prinCipal rech&rge areas if facilities are designed. constructed. maintained. and operllted to prevent accidental releases. . Justification The criterion is consistent with the DHS criterion with the exception of two changes. Critcrion Il(a) includes reference to regional aquifers for information purposes. These basins are identified as regional aquifers in the County General Plan and the specified bulletin. Criterion II (b) includes reference to "designed. constructed. maintained. and operllted". This language is consistent with language found in the CCR. Both II (a) and (b) reflect the purpose and intent of the DHS criterion. 10. PERMEABILITY OF SUJtFICIAL MATERIALS a. Land disDosal hcilitics shall be located in areas where underlying geology provides impermeability meeting the requirements of the SWRCB. (Pursuant to Title 23. Subchapter IS. Section 2531 (b) (I) of the California Code of Regulations). b. Treatment. reevelin2. !tor82e :inti tran!l;rer faeilities may be sited in &reas where soils are permeable if adequate engineered features such as spill containment. monitorin&. and inspection measures are included in the project design and construction. . - Justification The recommended criterion is consistent with the DHS criterion. 11. NON-ATTAINMENT AIR AREAS SDeciried hazardous was:te facilities may be located in non-attainment areas if the facilities meet the plans and regullltions of the air quality agency of each district. J ustifica lion The criterion is consistent with the DHS criterion although the need for a risk assessment is included in P/A-s-.. The County of San Bernardino is served by two separate air quality districts. The Valley portion of the County and the mountain slopes surrounding the valley are within the South Coast Air Quality Management District. an air basin which exceeds the national ambient air quality standards for o:zone. oxides of nitrogen carbon monoxide and particulate matter. The San Bernardino desert areas are within the jurisdiction of the County Air Pollution Control District certain areas and are non-attainment for o:zone. . - E-6 e e e . . 12. CRITERIA POLLUTANTS IN PREVENTION OF SIGNIFICANT DETERIORA nON (PSD) AREAS SDeciried hazardous WR.ste facilities may be located in PSD areas if facilities meet the plans and regulations of the air quality agency of each district. These facilities, however, may not be located near or . within national parks, wilderness and memorial areas, and other similarly dedicated areas, as specified in the Clean Air Act. J ustific:a tion The criterion is consistent with the purpose and intent of the DHS criterion. (See previous discussion on non-attainment areas as well.) PSD areas are divided into three classes, each with maximum allowable increases in pollutant concentrations over baseline conditions. Class I PSD areas, the most restricted areas include international parks,. natural wilderness areas exceeding 6000 areas and other areas approved by the EP A. Designated Class I areas within the County include the Joshua Tree National Monument and the Cucamonga and San Gorgonio National Wilderness Areas. 13. WETLANDS SDeeiried hazardous wllste facilities shall be prohibited from impa.iring the viability of wetlands such as saltwater, fresh water, and brackish marshes, swamps, and bogs inundated by surface or groundwater with a frequency to support, under normal circumstances, prevalence of vegetative or aquatic life which requires saturated soil conditions for growth and reproduction, as defined in general, regional, state, and federal plans. A protective buffer zone shall be established based on a biOlogical resour~e study and risk assessment. J ustific:a tion The DHS criterion has been modified to be consistent with County policy. Reference to prohibiting the impairment of wetlands has been added. The criterion. however, provides flexibility in determining an adequate distance from wetlands and does not prohibit siting of facilities. The County General Plan identifies several areas in the County for preservation; these areas include wetlands. These areas serve al habitat for species that may become endangered as a result of continued habitat loss. The location of a hazardous waste management facility in an area of biological value could result in the loss of critical habitats, loss of wetlands for groundwater recharge, and an increase in the potential for pollutant dispersal in ground and surface waters. Biological Resource Policy BI-I requires the protection of these areas by requiring that mitigation measures and buffer areas be established based on a biological resource study. Specifically, the policy recommends that proposed projects should "Enhance the viability of habitat areas through access restrictions, E.' . . . buffer areas, open space designations, and improvement projects (...ater, soil, and. vegetation).' See discussion below as ...ell. ~ / 14. HABITATS OF THREATENED, RARE. OR ENDANGERED SPECIES SDec:iried hazardous wa$te facilities shall be prohibited from impairinl the viability of habitats of threatened, rare, or endangered species as defined in general, regional, state, and federal plans. A protective buffer zone shall be established based on a biological resource: study and risk assessment. Justification The DHS. criterion has been modified to include reference to prOhibiting the impairment of threatened, rare, or endangered species. R.eference to 'rare' species ...as also added to account for those rare species that have been designated for protection by state and federal plans. The criterion provides flexibility in determining an appropriate distance from these sensitive species and does not prohibit the siting of facilities. State and federal la...s protect the habitats of threatened, rare, and endangered species. The U.s. Department of Interior, Fish and Wildlife Service, in its comments on the draft CHWMP stated their support for protecting habitat and ensuring their survival. Further, the Department sta ted that' _the Federal Endangered Species Act requires that the impacts to listed species be avoided. Mitigation other than avoidance is generally not permissible under Federal La..... - Since about 75% of the County is under federal jurisdiction, areas in the County have been designated as environmentally sensitive areas by different federal agencies. Federal plans like the BLM. California Conservation Area Plan designates unusual plant assemblies and areas of environmental concern. The U.s. Forest Service, Land Management Plan, designa tes wilderness areas and sensitive species. The County General Plan includes reference to over 20 threatened, rare, and endangered plants and animals ...hich are protected by state and federal plans. Because reference to considering federal plans was not included in the DHS suggested criterion, reference to the need to review federal plans and the inclusion of 'rare' species was added. Furthermore, the County General Pia n has a goal to 'Protect rare or endangered species and protect areas of special habitat value.' Biological R.esource Policy (BI-I) requires the protection of threatened, rare, and endangered species by requiring that mitigation measures and appropriate buffer areas be established based on . a biological resource report. -, E-S ,----- I e e e . . I S. PRIME AGRICULTURAL LANDS SDeciried ha~2rdous waste racilities may Dot be sited OD prime agricultural lands as defined in California law and adOPted local land use plans unless an overriding public need is served. When siting hazardous waste management facilities in these areas, overriding public service needs must be demonstrated. Justification The recommended criterion is consistent with the DHS criterion. 16. RECREATIONAL, CULTURAL, OR AESTHETIC AREAS Soecified haurdous wute facilities shall not be located in recreational, cultural, or aesthetic areas except low volume transfer and storage facilities which are necessary to handle hazardous wastes generated by visitors, workers. or residents in these areas. Recreational. cultural, and aesthetic resource areas include public and/or private lands having local. regional, state, or national significance, value or importance, such as: national, state, regional, county and loeal parks and recreation areas; historic resources; wild and scenic rivers; scenic highways; ecological preserves; public and private preservation areas; and other lands of local, regional, state. or na tional significance. J ustifica tion The recommended criterion is consistent with the DHS criterion. (The description of the recreational, cultural, and aesthetic resources was takcn from the Southern California Hazardous Waste Management Project, Siting Manual. page 1-42.) 17. AREAS OF POTENTIAL MINERAL DEPOSITS SDeeiried ha:lardous waste faeilities should Dot be located so as to preclude extraction of minerals necessary to sustain the economy ,?f the state. Justification 'rhe recommended criterion is consistent with the DHS criterion. I S. MILITARY LANDS Public specified hazardous waste facilities shall not be sited on military lands pursuant to DOD policy. E-9 . . . Justification Minor changes were made to the DHS criterion. The purpose and intent of the DHS criterion has not changed. 19. PROXIMITY TO AREAS OF WASTE GENERATION a. Land disDonl facilities may be located. more distant from waste generation sources than other facilities because of their requirement for larger land and buffer areas. b. Treatment reevclin2 stor82e and transfer 'acilities shaU be close to hazardous waste leneration sources to minimize: the risks of transportation. Justification Minor chanles were made to the DHS criterion. The purpose and intent of the criterion has nOI changed, however. 20. PROXIMITY TO MAJOR TRANSPORTATION ROUTES Sneeiried hazardrms W8.ste facilities shall bave good access to aDd from major transportation routes (state or interstate divided highways). . Justification The criterion is very similar to the one proposed in the luidelines with a few minor changes to the introductory lanluale. The criterion is stated as a separate requirement while DHS combines the discussion regarding distance to major and minor routes. 21. MINIMIZE TRANSPORT THROUGH MINOR ROUTES Sneeiried hazardous waste facilities should be sited so that road networks leading to major transportation routes do not pass through residential neighborhoods, should minimize: residential frontages, and should be demonstrated to be safe with regard to road design and construction, accident rates, excessive traffic, etc. Justification The criterion is very similar to the one proposed in the guidelines with a few minor changes to the introductory language. The criterion is stated as a separate requirement while DHS combines the discussion regardinl distance to major and minor routes. e .._' E-IO e e e . . 22. LOCATIONAL RESTItlCTlONS DUE TO TRANSPORTATION ROUTES a. SDeeiried ha~tlrdous WSl!!:te 'acilities shall Dot be loeated where highways 5&, 62, and 71 are used as major transportation routes unless a study or transportation routes as specified in P/A.lo-3 identifies mitigation measures which ean be implemented to make the particular route suitable ror iu use as a major route. b. . Low volume transfer and storaRe r.eilities may be located in these areas ir necessary to manage the hazardous wastes rrom that area. Justification The criterion allows ror mitigating the condition or the routes and. thus, is not prohibitive. It allows ror the development of mitigation measures to make the route suitable for a particular project. The CHWMP in its discussion of transportation has identified several highways or concern. Highways 5&. 62. and 71 should not be used as major transportation routes because they are not designed to accommodate heavy vehicles, they hive high accident rates, and rront residential and commercial land uses (Highway 62). Highway 5& will undergo repair and change rrom a two lane to a rour lane route. This improvement is scheduled ror completion in 1991. E-II e e e . . APPENDIX F GENERAL DESIGN A TJON MAPS Note: The maps arc included Cor illustrative purposes only. The County oC San Bernardino is currently in discussioD with the State Department oC Health Services OD the manner in which the maps should be presented. The inCormation used to prepsrc the CHWMP maps is available Cor public: revicw at the County oC San Bernardino Depsnmcnt oC Environmental Health Services. ,e -e ,e '\ . . GENERAL DESIGNA nON MAPS AB 2948 (Chapter 1504. Statutes of 1986) as amended by SB 477 (Chapter 1167, Statutes of 1987) requires that counties identify general areas in the county where hazardous waste facilities could be located. The Act specifies that: " An identification of those hazardous waste facilities that can be expanded to accommodate projected needs and an identification of general areas for new hazardous waste facilities determined to be needed. In lieu of this facility and area identification, the Plan may instead include siting criteria to be utilized in selecting sites for new hazardous waste facilities. If siting criteria are included in the county hazardous waste management plan, the plan shall also designate general areas where the criteria might be applicable." The County prefers to focus on the use of the siting criteria as opposed to the general designation maps for the siting of facilities because not all of the siting criteria could be -mapped. The maps should be used for illustrative purposes only. They demonstrate that after applying available siting information general areas exist where facilities could be sited. The siting criteria as described in Chapter 5 and the policies of the General Plan as well as the provisions of the Development .Code (zoning ordinance) will be used to determine the meriu of a project proposal. Thc General Designation Map (Figure I) was developed by mapping available siting information on a county-wide basis. Table F-I provides additional information on the mappable criteria. The information that was mapped includes: federal lands (including military facilities, Indian lands and reservations, and Bureau of Land Management (BLM) lands). county and state parks, areas of critical concern as defined by the BLM, seismic safety zones, major transportation routes, national scenic areas. national monuments, and rare and endangered species. T\le criteria which could not be mapped on a countywide basis (and at this scale) includes: proximity to residences proximity to immobile populations proximity to public facilities flood plain areas unstable soils F.l . . depth to ground ....ter perme.bility of surfiei.l materi.ls non-.tt.inment .ir are.s PSD areas ...etl.nds prime .gricultur.1 lands areas of potential mineral deposits e A large portion of the County is ...ithin the jurisdiction of the federal government. Large federal land bolders include the BLM, the Department of Defense, and the U.s. Forest Service. Indian lands and reservations are also a signifieant component of the County. Federal lands are not subject to l.nd use control by either the County or the cities. Furthermore, the policies of these agencies restrict use of certain federal lands for hazardous ...aste facilities. thus, these lands represent restricted areas. The BLM may consider the sale or land exchange of v.rious parcels if proposals are consistent ...ith BLM plans and policies. Three geographic regions .re found in the County. These include a rapidly urbanizing valley, a mountainous .rea, and a vast, sparsely- populated desert (Figure F-2). The desert comprises the largest area in the County. A variety of land uses exist in the desert area such as mining, - defense training and testing, and recreation. For the most part the desert region is zoned R.ural Conservation District; the revised County General Plan ...ilI Change the zone designation to R.esource Conservation District. This area ...ould be the most appropriate location to site land disposal facilities because of the need for large land areas. Treatment, recycling, storage, and transfer facilities should be sited near the waste generation sources, urban and rural areas (Figure F.3). e ~ F.2 :i e . . . ~ ~z- .. .. = .. i: t:.. ~ >. - = :z 0 0 '" >- - u !-< '" E 0 < Q. :z .. = C> c:i t:.. C,.,.) - u .... Vol , C> ~ ~ I,;.. .. ::2: Q -- CI - ..l .. = - 0:::: < III = -c::: =' - - ::2: ~ - 0:::: :z .. 0 r-_"l .~ J,:.. CO c:i :z: -c::: 1:.1:) e .- -." . .. I/. = Q .S ..- = .. .0 .- u 1/...., -c ~ CD -0) CD ...J - ~ .~ j ~ ~ : e Cl & ill ~ ~ a: .J (J III :2 :l ... It (J Z rr 0 i III III III A,.;;j ... A, ID e ~ J: i::i (J Q o < .... ... ~ ... < :l III Cl )0 )0 ~ ~...'fIt . . I ! . . " i" I Ii. . q . I i~ i j I dOli i Ii u I II I I fl -...~..... .. i ~ ;;! . L i I! ~ i i . i.. li!i~ g i i! 'I Eeeeee c:: t.l iffi," ! ., f ! i eeese II ... ,Z III ~ i < 0 0 l!! ~ ::f < " ... t) a: < III Z Z II 0 ~ l!! ~ : rr [lz, ~ ~ .~ Oil!, ' ; i~ .0::::.-:-::- .O;JS.!<Oo'o!iJ.o -':0:.0-:::.,,- ~:::::;::::::. ~~~*~~i: ~~=i~~~~. ;:-:.:...~:::::.:.: >>x-:-:-...... . i .' I ~ i! I I i . I ! r I , ~ ee@e~ r I I i J I i I I I ! r I. t.! ,. o@eee . ! i ! ' :I. f . J I, I " r :l I I , . . I I I '1 '. f, I . I o C)'SO s i . . f ! I r i' I r I 0'00 II I ~! .... II t) Z :l J 'if II OJ 0 III } 1:.. ~ ~ :1 i'll! ,a: S I ! ~ 11t ! I III ~i 0 . 0 ~iJliill 0 '0' 0 I 0 0 -olll.UIB .0 0 0 0, 0 IfHj ,llf I 'Hi! 1:1" 'I U : 1! I. o. e ~ e '. . . . . TABLE F-I MAPS USED FOR EVALUATING SmNG CRITERIA Base Maps: Taken from GIMS. and Data Systems. Alquist-Priolo Special Snadies Zone Data Systems. - based on maps issued by the State Geologist. State Mining and Geology Board pursuant to Section 2622, Division 2. Chapter 7.5 of the Public Resources Code Water Basin Exclusion Map Bulletin .11&, 1975, California Department of Water Resources Endangered Species Habitat (except tortoise) Valley: Fred Hinshaw, Associate Planner, Environmental Analysis, San Bernardino County Office of Planning Desert: California Desert Conservation Area Plan, 1980, Department of the Interior, Bureau of Land Management, (Desert District, Riverside, Ca.) East Mohave National Scenic Area and ACEC's (Areas of Critical Environmental Concern) California Desert Conservation Area - 1982 Amended Plan, Department of the Interior, Bureau of Land Management Wilderness Study Areas California Desert Wilderness Inventor)', Final. Department of Interior, Bureau of Land Management, March 31, 1979. Military Bases - Data Systems National Forest - Data Systems Dcscrt Tortoise Habitat "Tortoise Density in the California Desert Conservation Area, Plate 202." Taken from: Berry, K.H~ and L.L. Nicholson, 1984. The Distribution and Dcnsity of dcsert tortoise populations in California in the 1970s. Chapter 2 in K.H. Berry (Ed), The Status of the Desert Tortoise (Gopherus agassiziz) in the United States, Report from Desert Tortoise Council to U.s. Fish and Wildlife Service, Sacramento Order .11310-0083-81 Transportation Routes. Data Systems · GIMS - Geographic Information Management System, San Bernardino Data Systems - County Department of Land Management, Office of Planning F-5 . SAN BERNARDINO COUNTY GEOGRAPHIC REGIONS DESERT IlILa" I . ~ . .. . IOU.CI: &AN Ir.N,UDlMO =ovwrt . Filurc F.2 e e Source: 1979 Couuty of Sau Bcruardiuo Geueral PIau e F-6 . SAN BERNARDINO COUNTY GENERAL PLAN COUNTYWIDE DIAGRAM San Bernardino National Forest II ~...'.'-" t!!1J D Urban Rural Rural Conservation * MILIa- . I 0 . " . JOUlel: taN '11lII"A"DlNO OINIUL "-"I F-7 . Figure F.3 · This designation will change to Resource Conservation District as part or the update to the General Plan Source: 1979 County or San Bernardino General Plan . . ce APPENDIX G EXPENDITURE PLAN FOR THE HAZARDOUS SUBSTANCE CLEANUP BOND ACT OF 19&4 e e . . e Health and Welfare Agency Department of Healtll Services Toxic Substances Control Division EXPENDITURE PLAi'J FOR TI-IE HAZARDOUS SUBSTANCE CLEAl'JUP BOND ACT OF 1984 e e Revised January, 1988 (Origi.nally Published January 1985) Revision No. 3 Volume 2 Site-Specific W orkplans for the Abatement of Listed Hazardous 'Waste Sites . ** COUNTY: San Bernardino AIR FORCE PLANT 42 BARSTOW/MARINE CORPS LOGISTICS BASE CRAFTON-REDLANDS AREA D1\GGET AIRPORT FORT IRWIN NATIONAL TRAINING CENTER GENERAL ELECTRIC ENGINE MAINTENANCE CENTER GEORGE AIR FORCE BASE ISAAC COHEN AND SON, INC. KAISER STEEL SITE KOPPERS - ONTARIO MOJAVE NAVAL WEAPON CENTER - RANGE B NORTH SAN BERNARDINO AREA NORTON AIR FORCE BASE WESTERN STATES REFINING YERMO TRUCK STOP/GROUND WATER ** COUNTY: San Die90 APACHE SERVICES CAMP PENDLETON MARINE CORPS TRAINING CAMP CHATHAM BROTHERS BARRELS CORONADO NAVAL AMPHIBIOUS BASE EL CAPITAN QUARRY/EL CAJON MOUNTAIN MILL SITE IMPERIAL BEACH NAVAL STATION MIRAMAR NAVAL AIR STATION NORTH ISLAND NAVAL AIR STATION OMAR RENDERING DISPOSAL SITE OTAY SANITARY LANDFILL POINT LOY"", NAVAL COMPLEX SAN DIEGO NAVAL STATION SANTA YSABEL ** COUNTY: San Francisco BAY AREA DRUM COMPANY HUNTERS POINT NAVAL SHIPYARD ** COUNTY: San Joaquin ACME GALVANIZING AMERICAN MOLDING AND MILLWORK BREA AGRICULTURAL SERVICE, INC. GEORGIA-PACIFIC CORPORATION, TRACY KEARNEY-KPF I.AGUE SALES LIKA - FIELD AVENUE LIRA - NAVY DRIVE LODI AIRPORT LODI DOOR AND METAL COMPANY LUSTRE-CAL MARLEY COOLING TOWER COMPANY McCORMICK AND BAXTER 2-8 . palmdale Barstow e Redlands , Vicinity Da9get Fort Irwin Ontario Victorville Ontario Fontana Ontario China Lake San Bernardiho Fontana Yermo Chula Vista Escondido San Die90 Santee - Imperial Beach San Die90 San Die90 Chula Vista Chula Vista San Die90 San Die90 Santa Ysabel San Francisco San Francisco Stockton Stockton Linden Tracy Stockton Lathrop Stockton stockton Acampo Lodi Lodi Stockton Stockton e , , - ./ : e e e . . RESPO~SIBLE PARTY-LEAD SITE CLEANUP YORKPLAN ISAAC COHEN AND SON, INC. I. Site Information A. Location and Type of Site 717 South Taylor Avenue Ontario, CA 91761 San Bernardino Isaac Cohen and Son, Inc., has been in business for over 20 years . collecting and recycling metal and batteries. Lead and sulfuric acid were recovered from used batteries and recycled. . B. Description of Hazardous Yastes Hazardous wastes present on site include sulfuric acid, lead, arsenic, and waste oil. Sulfuric acid is moderately toxic, an irritant, and is reactive. Cutting oil is also moderately toxic and flammable. Lead and arsenic are both toxic and persistent in the environment. It is estimated that 300 cubic yards of contaminated material is present on site. C. Threat to Public Health and Environment A direct contact threat exists because of the proximity of the site to other businesses and residential areas. There is also a possibility of ground water contamination.. The degree of health hazard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. PHS policy is to evaluate all listed hazardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific hazardous substances if: 1) the site is not abated, 2) the substances migrate off site, and 3) .the substances at some point come into contact with human or environmental receptors. A-69 . . II. Site Status e ../ A. Status of Site Activitv The company has complied with past notices of violations issued by San Bernardino County Health Department and DHS. The responsible party has complied with Section 25359.5, Order to Post and Fence, and secure the site. A Remedial Action Order was issued in August, 1987. B. Projected Revenue Sources The responsible party is Isaac Cohen and Son, Inc.. DHS has budgeted $30,000 for oversight/monitoring of the responsible party's remediation activities. The responsible party will pay all costs of remedial investigation and remedial action including . reimbursement to DHS for its direct oversight costs plus staff costs and overhead. III. Project Co~letion Estimates The estimates below reflect completion of major site cleanup phases based on current information regarding this site and R1 cleanup plans and completed actions. e ,. Task Group Estimated Co~letion 1. Site Characteri:ation a) Remedial Action Order b) Remedial Investigation/ Feasibility Study Completed July 1988 2. Remedial Action Plan Oct. 1988 3. Remedial Action a) b.) c) Design Implementation Certification Nov. Jan. March 1988' 1989 1989 4. Cost Recoverv and/or Operation and Maintenance a) Cost Recovery b) Operation and Maintenance March 1990 N/A -- A-70 e e e . . RESPONSIBLE PARTY-LEAD SITE CLEANUP YORKPtAN KAISER STEEL SITE 1. Site Information A. Location and Type of Site 9400 Cherry Avenue Fontana, CA 92335 San Bernardino The Kaiser Steel facility is located on approximately four square miles of land. The facility was a former integrated steel production plant that operated from 1942 to 1983. Parcels of the property have been leased to other private parties. Much of the site is unoccupied and has areas which may contain hazardous wastes. These areas include unlined tar pits, chromium reduction ponds, and slag piles. The Department became fully aware of the presence of potential hazardous wastes in 1985 when asbestos and liquids from a benzol production area were released during demolition. Kaiser Steel is proposing that the facility be developed into an industrial park. B. Description of Hazardous Yastes The following hazardous substances were, among others, handled on the site during its years of operation: chromic acid, calcium carbide, polychlorinated biphenyls (PCBs), chromic hydroxide, asbestos, hydrochloric acid, ferric chloride, and oily wastes. The following hazardous wastes, among others, were released on the site after the facility was closed: asbestos, acenapthylene, anthracene, benzo(a)anthracene. benzo(a)pyrene. chrysene. fluorene. fluoroanthene, phenanthrene, pyrene, biphenyl, dibenisfuran, indene, and methyl naphthalene. These compounds have a wide range of potential health effects. They are toxic, some are corrosive, have central nervous system and respiratory effects and a number are known or suspected carcinogens. C. Threat to Public Health and Environment The site overlies the Chino Yater Basin, which is a source of drinking water for approximately 500,000 people. An intermittent flow storm channel traverses the property and may receive contaminated runoff from the site. The channel ultimately flows into the Santa Ana River which recharges drinking water aquifers downgradient. Disturbance of contaminated soils may result in a release of adverse air emissions that could expose workers and the public. The demolition of structures insulated by asbestos has exposed workers to the hazardous substance. 1..74 . . The degree of health hazard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all listed hazardous waste sites for the peed to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific hazardous substances if: 1) the site is not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptors. e II. Site Status A. Status of Site Activitv Regulatory and enforcement efforts are being undertaken by DHS, the R~QCB, EPA, and the San Bernardino County Environmental Health Department. Kaiser Steel has submitted a site investigation work plan to the involved agencies. The company has filed for bankruptcy and will be identifying additional financing through partnerships. B. Projected Revenue Sources The responsible parties are expected to enter into an enforceable agreement with DHS for oversight/monitoring of their cleanup efforts. DHS has budgeted $650,000 for related direct costs. DMS will recover 100 percent of direct costs plus staff costs 'and overhead related to the project. The responsible parties will pay all costs associated with site cleanup. - --.;'. III. Project Completion Estimates The estimates shown below reflect completion of major site cleanup phases based on current information regarding this site and responsible party cleanup plans and completed actions. e A-75 . e Task Group 1. Site Characterization a) Remedial Action Order b) Remedial Investigation/ Feasibility Study 2. Remedial Action Plan 3. Remedial Action a) Design b) Implementation c) Certification 4. Cost Recovery and/or Operation and Maintenance a) Cost Recovery b) Operation and Maintenance e e A-76 . Estimated Completion Completed June 1991 May Oct. May Dec. 1992 1992 1997 1997 May 1998 20+ years ,e e e . . RESPONSIBLE PARTY-LEAD SITE CLEANUPYORKPLAN GENERAL ELECTRIC ENGINE MAINTENANCE CENTER I. Site Information A. Location and Type of Site 1923 East Avion Street Ontario, CA 91761 San Bernardino This facility maintains and overhauls aircraft engines. B. DescriPtion of Hazardous Yastes About 6,000 gallons of hazardous waste were disposed of in dry wells. There is an estimated 600 cubic yards of waste and contaminated soil on site. Results of a 1987 investigation indicated the presence of l,l,l-trichloroethane (TCA) , tetrachloroethene (PCE) , chloroform, napthalene, 2- methylnapthalene, and volatile aromatics (xylene, toluene, ethylbenzene) in soils near the dry wells. These compounds are toxic, some are potential carcinogens, and they have a wide range of respiratory and central nervous system effects. C. Threat to Public Health and Environment The main concern is the potential for contamination of th~ ground Water. The degree of health hazard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all listed hazardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific hazardous substances if: 1) the site is not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptors. A.263 . . 11. Site Status e A. Status of Site Activity General Electric has performed some soil sampling (five borings in August of 1984, and 12 in February of 1987). General Electric is currently working on a proposal to further characterize the soil contamination at the site. B. Projected Revenue Sources Potential responsible parties are General Electric and the City of Los Angeles Pepartment of Airports. PHS will be issuing a remedial action order or entering into an enforceable agreement with the responsible parties. PHS has budgeted $50,000 for oversight/monitoring of cleanup activities. PHS will recover 100 percent of all costs related to this project. The responsible parties will pay all costs associated with site cleanup. III. Project Co~letion Estimates The estimates shown below reflect completion of major site cleanup phases based on current information regarding this site and responsible party cleanup plans and completed actions. e " . Task Groul> Estimated COlllf>letion 1. Si~e Characterization a) b) Remedial Action Order Remedial Investigation/ Feasibility Seudy Jan. June 1988 1989 2. Remedial Action Plan Sept. 1989 3. Remedial Action a) b) c) Pesign Implementation Certification Pee. June Aug. 1989 1990 1990 4. Cost Recovery and/or Ofleration and Maintenance a) Cost Recovery b) Operation and Maintenance Aug. 1991 N/A e A.264 . . / ~ DETAILED SITE EXPENDITURE PLAN CRAFTON-REDLANDS AREA I. Site Information A. Location and Tvpe of Site Redlands & Vicinity, CA San !ernardino 92374 This site" is an area of ground water contamination in the Bunker Hill ground water basin. In the past four years, the Redlands Municipal Water District has removed five domestic supply wells from production because of trichloroethylene (TCE), tetrachloroethene (PCE), and dibromochloropropane (DBCP) contamination. This site covers two zip code areas-- 92374 and 92373. B. Descri~tion of Hazardous Wastes e There are levels of TCE and DBCP above the State's health-based action level for drinking water at this site. TCE was a degreaser used in large quantities in commerical, industrial, and aerospace applications. It is no longer commonly used for such purposes. TCE migrates readily through soil and into ground water. DBCP is a nematocide, formerly used as a soil fumigant on citrus and other crops. These compounds are toxic, may cause central nervous system effects and are animal carcinogens. c. Threat to Public Health and Environment Ground water in the !unker Hill basin is of high natural quality. It is readily available for the current demand in the area. There is evidence that suggests the contamination may be moving in the direction of well fields serving the cities of Colton, Lome Linda and Riverside. The population served by wells potentially affected by the contamination is approximately 200,000. Although there are currently alternate sources for the closed wells, continued spread of the contamination will reduce or eliminate these options, potentially creating a condition of imminent endangerment. It may be necessary to initiate initial remedial measures (wellhead treatment) if this condition is determined to exist. There is no known exposure at this time. e The degree of health hazard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all l~sted hazardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats A-439 . . described in ~hi. docUDen~ generally represent ~he potential impact of ~., long-term exposure ~o .pecific hazardous subs~ances if: 1) ~he site is no~ abated, 2) ~he .ub.~ances migrate off si~e, and 3) the'substance. at some poin~ come in~o con~act wi~h human or environmen~al receptors. II. Site S~a~. A. S~atus of Si~e Activity An in~eragency group consis~ing of ~e City of Redlands, Ci~y of Riverside, ~he RWQCS (San~a Ana Region), County of Riverside Heal~h Oepar~ent, and OHS (Sani~ary Engineering and TSCO) , are coordina~ing ~he charac~erization and mi~igation of ~he con~amination. The'RWQCS has direc~ed ~he Lockheed Corpora~ion and ~he Ciry of Redlands ~o under~ake ch.rac~eriza~ion activi~ies at two possible sources of contamination. The OHS-TSCO has compiled .nd interpreted .11 existing data for Phase 1 of the Remedial Investigation. Field site characterization activities were initiated in November, 1987. S. Projected Revenue Sources Potentially responsible parties have not as yet been identified. It may be nec....ry to exp.nd bond fund. if the po~enti.lly responsible parties cannot be definitly idantified or if they will no~ undertake the required activitie.. If bond funds ar. expended, ~e Department will und.rtak. co.t recovery at an appropriate time. OHS reevaluat.d the .ite Hazard Ranking (Mitre Kodel) in May, 1987 and on that basis the site may be recommended for ~e NPL. If proposed for ~he NPL (by EPA) , federal funds may be a viable source of revenue for ~e site. ~ "-. /. III. Project SudEet and Cash Flow Estimate. The cost estimates .hown below reflect only State costs for site cleanup including planned interim remedial me.sures. All ac~ivi~ies will be funded from bond sale proceeds to the extent that federal Superfund or responsible parry funding i. not available. ~ A-440 ' . . e Projected Estimated Task Group SUte Costs Completion 1. Site Characterization $ 2,000,000 a) Final Determination of N/A Non-Compliance b) Remedial Investigation/ July 1990 Feasibility Study 2. Remedial Action Plan $ 100,000 May 1991 3. Remedial Action $ 8,000,000 a) Design Oct. 1992 b) Implementation Nov. 1995 c) Certification April 1996 4. Cost Recoverv and/or Operation and Maintenance a) Cost Recovery April 1997 b) Operation and Maintenance 20+ years e TOTAL PROJECT COSTS $ 11,000,000 e A.44l e e e . . DETAILED SITE EXPENDITURE PLAN NORTH SAN SERNARDINO AREA I. Site Information A. Location and Type of Site San Sernardino, CA San Sernardino 924Ul This site is an area of ground water contamination in the Sunker Hill Ground ~ater Sasin in San Sernardino County. The site includes areas within the following zip codes: 92401, 92404, 92405, 92407, and 92411. In the past four years, the San Sernardino Municipal Yater District has removed fourteen domestic supply wells from production because of trichloroethylene (TCE) and tetrachloroethene (PCE) contamination. S. DescriPtion of Hazardous Yastes There are levels of TCE and PCE above the State health-based action level for drinking water at this site. TeE was a degreaser used in large quantities in commercial, industrial, and aerospace applications. It is no longer commonly used for such purposes. PCE is a similar de greaser and dry cleaning cOlllpound (commonly used). Soth compounds migrace readily through soil and into ground water, have a wide range of toxic effects, including effects on the respiratory and central nervous system. Soth are suspected carcinogens. c. Threat to Public Health and Environment Ground water in the Sunker Hill Sasin is of high natural quality. Fourteen domestic supply wells have been closed, and there is evidence that suggests that the contamination is moving in the direction of well fields serving the majority of the population of the cities of San Sernardino and Riverside. The population served by wells potentially affected by the contamination is at least 200,000. In November, 1986, DHS found the area to constitute an Imminent and Substantial Endangerment to public health and the environment. There is no known current exposure above the health-based action levels. The degree of health hazard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all listed hazardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific hazardous substances if: 1) the site is A.486 . . not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact vith human or environmental receptors. e ~ II. Site Status A. Status of Site Activity An interagency group consisting of the City of San &ernardino Municipal Yater District, the RYQC& (the Sante Ana region), the San &ernardino County Department of Health Services, and DHS (Sanitary Engineering &ranch and TSCD) are coordinating an effort for characterizing and mitigating the contamination. The DHS . TSCD has compiled and interpreted all existing data for Phase 1 of the Remedial Investigation. Field site characterization activities vere initiated in November, 1987. In October, 1986, DHS-TSCD entered into a contract vith the City of San &ernardino for initial remedial measures: the design, construction and installation of airstripper tovers in two locations. The tovers vill replace the full capacity of the City's vater supply (25' vas lost vhen the fourteen vells vere removed from use). Construction vas initiated in mid-May, 1987. &. Prolected Revenue Sources It appears that it vill be necessary to utilize bond'funds to remediate this site. Attempts to idantify potentially responsible parties (PRPs) have not been successful as yet end are still in progress. The Department vill undertake cost recovery action at an appropriate time if possible, hovever, definitive identification of PRPs may not be possible for this site. DHS reevaluted the site Hazard Ranking (Mitre Model) in Kay, 1987 and on that basis, the site (or,a portion of the site) may be recommended for the NPL. If proposed for the NPL (&Y EPA) , federal funds may be a possible source of revenue for the site. - III. Prolect &ud~et and Cash Flow Estimates The cost estimates shown below reflect only State costs for site cleanup. All activities vill be funded from bond sale proceeds (to the extent that federal Superfund or responsible party funding is not available). e A-487 . e . Task Croup 1. Site Characterization a) Final Determination of Non-Compliance b) Remedial Investigation/ Feasibility Study 2. Remedial Action Plan 3. Remedial Action a) Design b) Implementation c) Certification 4. Cost Recoverv and/or Operation and Maintenance a) Cost Recovery b) Operation and Maintenance TOTAL PROJECT COSTS e e $ 11,100,000 A-4BB . Aug. 1997 20+ years . . FEI>EL\L FACILITY SITE CLEANUP \lORXPlAN NORTON AIR FORCE BASE I. Site Information A. Location and Tvpe of Site Norton Air Force !ase CA 92409-5045 San !ernardino This site is a U.S. Air Force Military Airlift Command !ase. Headquarters for the Kilitary Air Command is Scott Air Force !ase. B. I>escription of Ha:ardouS \lastes Past disposal activities on base have caused the release of large quantities of fuels, solvents, and heavy metals to the soil. There is a high potential for ground water contamination. \lells on base are contaminated with chlorinated hydrocarbon solvents. e C. Threat to Public Health and Environment Major public drinking supply wells are as close as 500 feet to areas of ~, wastes disposed on site. I>rinking water supplies are threatened. ,.., , The degree of health ha:ard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. I>HS policy is to evaluate all listed ha:ardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific ha:ardous substances if: 1) the site is not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptors. II. Site Status A. Status of Site Activity This site has been added to the National Priority List. Phases II and IV of the Air Force assessment studies are in progress at 23 areas on site. Interim Remedial Measures may be proposed for area 17 to prevent contamination of water supply wells. DHS will enter into a three-way agreement with EPA and the Air Force to characteri:e and mitigate the contamination. A-780 e / e e e . . II. Site Status A. Status or Site Activity The site has a history or mismanagement of ha~ardous waste and a record of enforcement actions by local authorities and the Regional Water Quality Control Board (RWQCB). DHS inspected the facility in April, 1985 and obtained samples in April and Kay, 1985. The racility was directed by DHS to mitigate contamination. The company subsequently filed Chapter 11 bankruptcy. At the request of the RWQCB and local health agencies DHS performed an IRK consisting of drum repackaging and providing guard service. EPA completed IRK actions and removed the majority of wastes. B. Projected Revenue Sources The parent corporation of Western States is Veta Grande Companies, Inc., 19400 Business Center Drive, Northridge. CA 91324-3505. The responsible parties have, thus far, refused to mitigate the site. It appears at this time that it will be necessary to utili~e bond funds to remediate this site. If bond funds are expended, DHS will undertake appropriate cost recovery action. This site has not been identified as an NPL site, nor does it appear to be likely NPL candidate in the future. Federal funds were made available for immediate removal activities. DHS'costs for interim measureS Were approximately $30,000. III. Project Bud~et and Cash Flow Estimates The cost estimates sho~ below reflect only State costs for site cleanup. All activities will be funded from bond sale proceeds (to the extent that federal Superfund or responsible party funding is not available). A-SOl e I . A-502 . .' . ..> . . . FEDERAL FACILITY SITE CLEANUP VORKPLAN AIR FORCE PLANT 42 I. Site Information A. Location and Type of Site Palmdale Airport Palmdale, CA 93550 San Bernardino Air Force research and development facility. B. Descri~tion of Hazardo~s Vastes Plant 42 is an Air Force research and development facility. Twenty-three contaminated areas were discovered in the initial assessment phase. Contaminants are f~els, oils, solvents, paint, soil sl~dges, acids, heavy metals, and polychlorinated biphenyls (PCBs). The large variety of wastes have a wide range of potential health effects. Some compo~nds are toxic, some flammable orignitable, some are respiratory or central nervo~s system depressants, some may affect liver function. PCB is a s~spected carcinogen and a known teratogen. Actual effects are dependent on specific compounds , 'concentrations, and expos~re. C. Threat to P~blic Health and Environment Tne types and q~antities of wastes released ground water and drinking water supplies. at this time. on base pose a threat to There is no known exposure The degree of health hazard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all listed hazardous waste sites for the need to take .action to abate any ac~te p~blic health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term expos~re to specific hazardous s~bstances if: 1) the site is not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptors. A-691 . . II. Si~e Status . A. S~a~us of Si~e Ae~ivity The Installation Restoration Program (IRP) has been initiated at this base. Currently, the program is in the Confirmation Quantifieation (Site Investigation) Phase of the mitigation proeess. !. Projeeted Revenue Sourees The Department of Defense will provide funding for site eharacterization and remedial actions. III. Projeet Com~letion Estimates DHS has budgeted $100,000 from the bond fund to provide for private consultant assistanee to DHS oversight staff. DHS will seek eost reeovery from the U.S. Government. Task Gro~ Estimated Co~letion . 1. Site Charaeterization a) Remedial Aetion Order b) Remedial Investigationl Feasibility Study July 1991 April 1994 2. Remedial Action Plan Oct. 1994 3. Remedial Action a) b) c) Design Implementation Certification April Oet. Dee. 1995 1996 1996 4. Cost Recovery and/or ~eration and Maintenanee a) Cost Reeovery b) Operation and Maintenanee Dee. 1997 N/A - " .....: A.692 e \ ~. e Ie \-- . . FEDERAL FACILITY SITE CLEANUP \.10RKPLAN BARSTO\J;MARINE CORPS LOCISTICS BASE I. Site Information A. Location and Tvpe of Site Marine Corps Logistics Base Barstow, CA 92311 San Bernardino The Marine Corps Logistics Base in Barstow consists of three areas: Nebo, Yermo, and the rifle range. The base'is located in San Bernardino County, California, in the Mojave Desert, adjacent to the Mojave River. B. DescriPtion of Ha~ardous \Jastes A total of 33 sites that received ha~ardous wastes were identified at the base. The history of waste disposal at the site indicates that waste water treatment plant sludges, pesticides, waste oil solvents, gasoline, diesel fuel, and paints are present. The large variety of wastes have a wide range of potential health effects. Some compounds are toxic, some flammable or ignitable, some are respiratory or central nervous system depressants, some may affect liver function. Some solvents are suspected carcinogens. Actual effects are dependent on specific compounds, concentrations, and exposure. C. Threat to Public Health and Environment The initial assessment studies concluded that 4 of the 33 sites found at Marine Corps Logistics Base in Barstow pose a potential threat to human health or to the environment and warrant confirmation studies. However, DHS's review of the initial assessment study document indicated more than 4 of the 33 sites pose a potential threat to human health or to the environment. The primary concerns are ground water and direct contact. There is no known exposure" at this time. The degree of health ha~ard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all listed ha:ardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific ha~ardous substances if: 1) the site is not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptorS. A-69S . . II. Site Status A. Status of Site Activity The Installation Restoration Program has been initiated at this base. Currently the program is in the Phase I Initial Assessment study step of the mitigation process. B. Projected Revenue Sources The Department of Defense will provide funding for site characterization and remedial actions. III. Project Completion Estimates PHS has budgeted $100,000 from the bond fund to provide for private consultant assistance to PHS oversight staff. PHS will seek cost recovery from the U.S. Covernment. Task Gro\1ll Enimated Co=,letion 1. Site Characteri:ation a) Remedial Action Order b) Remedial Investigationl Feasibili~Study 1989 1992 May Feb. 2. Remedial Action Plan Aug. 1992 3. Remedial Action a) Design b) Implementation c) Certification Feb. Aug. Oct. 1993 1994 1994 .4. Cost Recovery and/or Operation and Maintenance a) Cost Recovery b) Operation and Maintenance Oct. 1995 N/A A.696 . , e e e e e . . FEDERAL FACILITY SITE CLEANUP 1oI0RKPUN GEORGE AIR FORCE BASE I. Site Information A. Location and Tvpe of Site Victorville, CA San Bernardino 92394 The site is a U.S. Air Force Base. B. Description of Hazardous loIastes Fifty-four potentially hazardous areas were identified in the initial assessment study. Phase II of the Installation Restoration Program has documented ground water contamination from trichloroethylene (TCE) on and off site. Hazardous wastes disposed of on site include asbestos, pesticides, paints and paint sludges, fuels, oils, leaded tank bottoms, explosives, polychlorinated biphenyls (PCBs), cleaning solvents, acids, metals, and low-level radioactive wastes. The large variety of wastes have a wide range of potential health effects. Some compounds are toxic, some flammable or ignitable, some are respiratory or central nervous system depressants and some may affect liver function. PCB is a suspected'carcinogen and a known teratogen. Actual effects are dependent on specific compounds, concentrations and exposure. C. Threat to .Public Health and Environment Hazardous wastes released on the site have contaminated the ground water. Contaminants are migrating off site and are a threat to the water quality and the drinking water supplies. There is no known exposure ae chis time. The degree of health hazard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all iisted hazardous waste si tes for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific hazardous substances if: 1) the site is not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptorS. A- 735 . . II. Site Status e A. Status of Site Activity The Installation Restoration Program has been initiated at this base. Currently the program is in phase IV.A (Feasibility) of the mitigation process. George ~F! is undertaking ground water mitigation pursuant to an RWQC! abatement order. Air stripping has been chosen to remediate the ground water contamination. !. Pro;ected Revenue Sources !he Department of Defense will provide funding for site characterization and remedial actions. III. Pro;ect Com~letion Estimates DMS has budgeted $100,000 from the bond fund to provide for private consultant assistance to DMS oversight staff. DMS will seek cost recovery from the U.S. Government. e Task Grou~ Estimated Co~letion 1. Site Characterization. a) Remedial Action Order b) Remedial Investigation! Feasibility Study Sept. 1989 June 1992 2. Remedial Action Plan Dec. 1992 3. Remedial Action a) b) c) Design Implementation Certification June Dec. Feb. 1993 1994 1995 4. Cost Recovery and/or ~eration and Maintenance a) Cost Recovery b) Operation and Maintenance Feb. . 1996 20+ years e A.736 . e e . . 11. Site Status A. Status of Site Activity Riverbank is conducting a remedial investigation to fully charaterize the extent of contamination. Off base domestic wells have been sampled quarterly since 1986. The Riverbank facility is also investigating and installing systems to recycle waste products. B. Proiected Revenue Sources The Department of Defense appropriates federal funds for the site characterization and remedial action at this site. State funds may be used for staff oversight activities. The Depar~ent of Health Services will seek funding from the EPA and cost recovery stipulated through the Remedial Action Order process. 111. Proiect Completion Estimates !he Department has budgeted $100,000 from the bond fund to provide for private consultant assistance to the DHS.oversight staff. The DHS will seek cost recovery from the U. S. Government. The schedule shown below is projected by the PHS staff based on current status of cleanup activities and other information developed by the military. Task Group Estimated Completion 1. Site Characterization a) Remedial Action Order b) Remedial Investigation/ Feasibility Study Oct. Feb. 1988 1989 2. Remedial Action Plan Oct. 1989 3.' Remedial Action a) b) c) Des i gn Implementation Certification Oct. April Aug. 1990 1992 1992 4. Cost Recovery and/or Operation and Maintenance a) Cost Recovery b) Operation and Maintenance Sept. 1993 20+ years A.783 . . DETAILED SITE EXPENDITURE PLAN \lESTERN STATES REnNINC e I. Site Information A. Location and TVDe of Site 10763 Poplar Avenue Fontana, CA 92335 San ~ern&rdino This facility formerly recovered precious metals from photographic film using a cyanide and acid leaching proc.... B. DescriPtion of Ha:ardous Yast.s Ha:ardous .Ubstances were .tored in various decomposing containers and tanks r..ulting in soil contamination. Soil contaminants include: cyanide .olids and liquids,. acids, metallic material., and volatile organic compounds (VOC.). Cyanide, including sodium cyanide, is highly toxic and reactiv.. In association with acid, which i. also found on sit., it may emit highly toxic hydrogen cyanide gas. Heavy metals may be toxic and they may accumulate in animal systems. VOC. may b. toxic, and they may have a wid. range of central n.rvous syst.m and r.spiratory .ff.cts. e "...,/ C. Threat to Public Health and Environm.nt Th.r. is thr.at of toxic air .missions, .urfac. wat.r runoff, and contamination of ground wat.r which is used ext.nsively for dom..tic supply in the ar.a. There is no kno,,'n exposure at this time. The degree of health ha:ard posed by chemical contamination of a site depends on the concentration of the material pre.ent and the duration of exposure. DHS policy is to evaluate all.listed hazardous vaste sites for the need to take action to abate any acut. public h.alth or environmental threat. posed by a site. Therefore, the threat. described in this document generally represent the potential impact of long-term expo.ure to specific ha:ardous .Ub.tance. if: 1) the .ite is not abated, 2) the .ub.tance. migrate off .ite, and 3) the .ub.tances at some point come into contact vith human or .nvironmental receptor.. ~. 1..500 e a ". ~ e . . BACKLOG SITE CLEANUP PLANNING REPORT DAGGET AIRPORT I. Site Information A. Location and Type of Site Dagget, CA 92327 San Bernardino This site is a former military airfield which has been turned over to San Bernardino County. The Army and the Navy lease the area from the County to perform helicopter maintenance. B. Description of Hazardous ~astes The types and volumes of hazardous wastes present at the site are unknown at this time. The suspected contaminants are solvents, spent fuels, heavy metals, explosives, and pesticides which are frequently associated with the operational activities at these types of facilities. ~. Threat to Public Health and Environment There may have been discharges to surface impoundments and landfills at this facility. The full extent of the threat to public' health and the environment is not known at this time pending further documentation of volume, type, and extent of migration of the wastes on site. Facilities of this type have historically handled hazardous wastes in a manner which resulted in uncontrolled releases to the environment which , pose different levels of threat based on the extent of reiease and proximity of human populations and sensitive environments. There is no known public exposure at this time. DHS will monitor conditions at this site to detect any change in public health status. If a change in status should occur, DHS will schedule an appropriate response action and notify the Legislature. The degree of health hazard posed by chemical ,contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all listed hazardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific hazardous substances if: 1) the site is not abated. 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptorS. A-896 . . II. Site SUtus A. Status of Site Activity The Installation Restoration Program (IRP) has not been initiated at this base. B. Projected Revenue Sources This site is projected for cleanup funded by responsible parties vith reimbursement to DHS for staff and related costs. Hovever, if the responsible parties fail to provide funding for cleanup another souree of funds viII need to be established. III. Cleanup Completion Estimates Based on limited information, this site appears to be a medium site. Since the information is limited, no eleanup estimates have been projeeted at this time. This site viII be targeted for eleanup in a later edition of the Expenditure Plan based on relative site cleanup priorities at the time of the update. A-897 . ~ ~ e e e . . BACKLOG SITE CLEANUP PI..A.NNING- REPORT FORT IRWIN NATIONAL TRAINING CENTER I. Si~e Informa~ion A. Loca~ion and Type of Si~e For~ Irwin, CA San Bernardino 92310 For~ Irwin is a U.S. Army training facili~y. B. Descrip~ion of Hazardous \Jas~es Fuels, oil, solven~, and muni~ions have been iden~ified a~ ~his site and are buried in landfills. DHS has received ~he Phase 1 Ini~ial Assessmen~ S~udy for For~ Irwin. The volumes of hazardous wastes present a~ the si~e are unknown at ~his ~ime. These compounds are ~oxic, may be igni~able, may genera~e soil gas, and some may be carcinogenic. c. Threa~ to Public Heal~h and Environmen~ There may have been. discharge ~o surface impoundments and landfills at this facility. The full ex~ent of ~he threat to public health and the environment is not known at this time pending further documentation of volume, type, and extent of migration of of the wastes on ~he site. Facili~ies of this ~ype have his~orically handled hazardous was~e in a manner which resul~ed in uncon~rolled releases ~o the environmen~ which pose differen~ levels of ~hreat based on ~he exten~ of release and proximi~y of human popula~ions and sensi~ive environmen~s. There is no known public exposure a~ ~his ~ime. DHS will moni~or condi~ions a~ ~his si~e ~o de~ec~ any change in public heal~h s~a~us. If a change in status should occur, DHS will schedule an appropria~e response action and no~ify ~he Legisla~ure. The degree of health hazard posed by chemical con~amination of a si~e depends on ~he concen~ra~ion of ~he ma~erial present and ~he dura~ion of exposure. DHS policy is ~o evaluate all lis~ed hazardous was~e si~es for ~he need ~o ~ake ac~ion ~o aba~e any acute public heal~h or environmental threats posed by a si~e. Therefore, the threa~s described in this documen~ generally represen~ ~he po~en~ial impact of long-term exposure ~o specific hazardous substances if: 1) ~he si~e is no~ abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptors. A-904 . . II. Site Status A. Status of Site Activity The responsible party is conducting a remedial investigation and a feasibility study with minimal DHS participation. B. Projected Revenue Sources This site is projected for cleanup funded by responsible parties with reimbursement to DHS for staff and related costs. However, if the responsible parties fail to provide funding for the cleanup another source of funds will need to be established. III. Cleanu~ Completion Estimates Based on currently available information, this site is projected-to be a large site which will require an estimated five years and 7.S months to complete from the date of cleanup initiation. This estimate is subject to change based on receipt of subsequent information. This site will be targeted for cleanup in a later edition of the Expenditure Plan based on relative site cleanup priorities at the time of the update. Therefore, no cleanup completion dates have been projected at this time. A.907 e ~ .~ . . . . . BACKLOG SITE CLEANUP PLANNINC REPORT KOPPERS - ONTARIO I. Site Information A. Location and Tvpe of Site 1200 Airport Drive Ontario, CA 91761 San Bernardino Koppers was a wood treatment and product storage site. Samples taken in July, 1985 contained elevated levels of chromium, arsenic, boron, and unspecified oil and grease. The site is located in a light industrial area bordering an agricultural area. B. DescriPtion of Ha~ardous ~astes Soil contamination with arsenic was found at five locations. Samples at three locations revealed elevated levels of boron in the soil. Oil and grease at high concentration was detected in the soil to a depth of six feet at another location. Chromium is a persistent toxic metal; some forms are carcinogenic. Arsenic, copper, and boron are persistent toxic metals. c. Threat to Public Health and Environment . The primary concern is potential contamination of the ground water. Depth to usable ground water is unknown at the site and probably varies widely due to seasonal rainfall and site location. There is no known public exposure at this time. DHS will monitor conditions at this site to detect any change in public health status. If a change in status should occur, DHS will schedule an appropriate response action and notify the Legislature. The degree of health ha~ard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all listed ha~ardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific ha~ardous substances if: 1) the site is not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptors. A-916 . . II. Site Status A. Status of Site Activitv DHS has worked with the RWQCB and the responsible party to develop and expand a remedial investigation. B. Projected Revenue Sources This site is projected for cleanup funded by responsible parties with reimbursement to DHS for staff and related costs. However, if the responsible parties fail to provide funding for cleanup, another source of funds will need to be established. III. Cleanup Completion Estimates Based on currently available information, this site is projected to be e small site which will require an estimated one year and 7.S months to complete from date of cleanup initiation. This estimate is subject to change based on receipt of subsequent information. This site will be targeted for cleanup in a later edition of the Expenditure Plan based on relative site cleanup priorities at the time of the update. Therefore, no cleanup completion dates have been projected at this time. A-917 . ~ ~ I I I Ie e e . . BACKLOG SITE CLEANUP PLANNING REPORT MOJAVE NAVAL IlEAPON CENTER - RANGE B I. Site Information A. Location and Tv~e of Site China Lake, CA San Bernardino 93550 The site is a military facility. B. Pescri~tion of Hazardous Ilastes The types and volumes of hazardous wastes present at the sit~ are unknown at this time. The suspected contaminants are solvents, spent fuels, heavy metals, explosives, and pesticides, all of which are frequently associated with these types of facilities. c. Threat to Public Health and Environment This Facility has several hazar~ous waste disposal areas and landfills which are suspected of causing ground water contamination. The full extent of the threat to public health and the environment is not known at this time pending further documentation of volume, type, and extent of migration of the wastes on site. Facilities of this type have historically handled hazardous wastes in a manner which resulted in uncontrolled releases to the environment which pose different levels of threat based on the extent of release and proximity of human populations and sensitive environments. There is no known public exposure at this time. PHS will monitor conditions at this site to detect any change in public health status. If a change in status should occur, DHS will schedule an appropriate response action and notify the Legislature. The degree of health hazard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all listed hazardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific hazardous substances if: 1) the site is . not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptors. A-924 . . II. Site Status e A. Status of Site Activity The Installation Restoration Program (IRP) has been initiated at this base. Currently the program is in the Initial Assessment Study (Preliminary Assessment) Phase of the mitigation process. B. Pro1ected Revenue Sources This site is projected for cleanup funded by responsible parties with reimbursement to DHS for staff and related costs. However, if the responsible parties fail to provide funding for cleanup another source of funds will need to be established. III. Cleanup COMPletion Estimates Based on currently available information, this site is projected to be a large site which will require an estimated 5 years and 7.5 months to complete from the date of cleanup initiation. This estimate is subject to change based on receipt of additional information. e . , The base will be targeted for cleanup in a later edition of the Expenditure Plan based on relative site cleanup priorities at the time of the update. Therefore, no cleanup completion dates heve been projected at this time. - A.925 . . . . . !ACKLOG SITE CLEANUP PLANNING REPORT YERMO TRUCK STOP/GROUND YATER I. Site Information A. Location and Type of Site 39753 Yermo Road Yermo, CA 92398 San !ernardino This inactive service station reportedly experienced chronic and significant fuel leakage during past operations. B. Description of Hazardous Yastes The Yermo Truck Stop is suspected as the source of motor fuel hydrocarbons detected in ground water nearby. !enzene, l,2-Dichlor- ethane and other petroleum hydrocarbons have been found. !enzene is a known human carcinogen. l,2-Dichlorethane is an experimental carcinogen in laboratory animals. C. Threat to Public Health and Environment Yermo municipal supply well number 4 is contaminated and there is potential for additional ground water contamination. Yermo Yater Company has been advised not to use the well unless in emergency and with blending to meet drinking water standards. There is no known public exposure at this time. DHS will monitor conditions at this site to detect any change in public health status. If a change in status should occur, DHS will schedule an appropriate response action and notify the Legislature. The degree of health hazard posed by chemical contamination of a site depends on the concentration of the material present and the duration of exposure. DHS policy is to evaluate all listed hazardous waste sites for the need to take action to abate any acute public health or environmental threats posed by a site. Therefore, the threats described in this document generally represent the potential impact of long-term exposure to specific hazardous substances if: 1) the site is not abated, 2) the substances migrate off site, and 3) the substances at some point come into contact with human or environmental receptors. A-980 . . II. Site Status ~ A. Status of Site Activity The RYQCB issued Cleanup and Abatement Order No. 86.15 to the owner of the Vermo Truck Stop to clean up the contamination. B. Prolected Revenue Sources This site is projected to be remediated by the responsible parties with reimbursement to DHS for oversight/monitoring and related costs. However, if the responsible parties are unable to fund site cleanup, another source of funds will need to be established. III. Cleanu~ Co~letion Estimates Based on currently available information, this site is projected to be a small site which will require an estimated 1 year and 7.5 months to complete from the date of cleanup initiation. This estimate is subject to change based on receipt of additional information. This site will ba targeted for cleanup in a later edition of the ~ Expenditure Plan based on relative site cleanup priorities at the time of the update. Therefore, no cleanup completion dates hava been projected at this tiDe. - ..-~. A-981 . . . APPENDIX H PUBLIC EDUCATION AND PARTICIPATION . I) CHWMP Advisory Committee Mcmbcn 2) Scbedule of Advisory Committee MeetiDgs 3) Scbedule of Publie Workshops 4) CommeDts Received at Publie Worksbops S) Scbedule of PDblie HeariDgs OD Draft CHWMP 6) Scbedule of Publie HeariDgs OD Draft CHWMP Before City DccisioD-Makcn 7) Sample Mailer aDd Flyer . e !he SaJl Bernardino County Hazardous Waste Man- azement Plan Advisory Co..ittee and the Department of Envirol1llental Health Services have scheduled six public workshops to hear c i tinn COllllDents and concerl\$ rerardinr: . the County Hazardous Waste Manarellent plan which is beinZ developed: and . issues to be addressed in the Environ- mental Impact Report on the Hazardous Waste ManaeelDent Plan. E..~amples of some critical issues which will be addressed in the Plan are: Waste reduction and recyclinz: Treatlllent plants and their locatiol\$; Disposal facilities for residuals fro. treatlllent: e r-\. ~ TraJlsportation of hazardous wastes: and Other issues raised by the public:. \JI DATES AND LOCATIONS OF PUBLIC WORKSHOPS September 25 9 a.ll. to noon San Bernardino. County Govel"lllllent Center ~ North Arrowhelld Avenue September 29 9 aJO. to noon Victorville. City Council ChaJDbers 14343 Civic Drive Septem ber 30 7 p.ll. to 10 P". Fontana, City Council ChaJDbers 8353 Sierra Avenue October 7 7 P". to 10 P". Yucca Valley Hirh School 7600 Safe Avenue October 14 7 p... to 10 P". Ontario. City Council Chubers 303 East B Street October 15 7 p... to 10 p... Barstow Junior llirh 1000 Araory Road e For further infol'llation. call Judy Orttunr at ~pp~r~ent of EnviroRmental Health Services. 714-387-4629 ,~\\llliJ~e ~t'/P/ -..... - ~ -- - - --s::. -=- .,,~ ~..... 111,111,\\\\~' SA:--J BER:\ARDINO COUNTY HAZARDOUS WASTE MANAGEMENT PLAN ADVISORY COMMITTEE A:\D DEPARTMENT OF ENYIRONME:-1TAL HEALTH SERVICES . . ";'''' .....t:.. ..... ... ~ ';," -..... '.,~, .:..~ . .." - t COUNTY OF SAN BERNARDINO '~\\III,~~/ . ENVlIIONMENTAL if JIf.. ~ ...~~,.':!~:_~!?:~ ~~~:y . ,,~V~..... ; /'llllll\\\~' IIICHAIID L. 1I0BEIITS. II.S.. ~; I I \ o;'.CUI< ENVIRONMENTAL HEALTH SERVICES ::J 31$ N_ _ho.d"_ . Soft _. CAl2d'U'IO . 17'.131'_ o 320 EoII ''0'' SIr"1 . 0........ CA II'M . 171.1 31""'0 :J 15505 CMc Driwo . V"ICI...... CA 12312 . 1.'112u.1'.' o Hazardous Waste' Toxics Centrol (714)387-4629 ".U.SE ~E". y TO "OD~ESS CHICKtD September 9, 1987 .......... ...........: -- -- ........... ........ c..... c........ c.. _ -- .... ,..... leA.......... --... - -- TO: COMMUNITY ORcaNIZA'1'IONS RE: POBLIC INVOLVEKEN'l' IN BAZARDOOS WAS'!'!: MANAG!:KEN'1' PLANNI1IIG Public concerns about the safe management of hazardous waste resulted in the passage of AB2498, the Tanner bill, 'by the Legislature last year. ~his legislation provided funding to enable counties to develop a comprehensive hazardous waste management plan including the siting of new treatment and disposal facilities and waste reduction programs. Public involvement in planning for how San Bernardino County will manage hazardous waste will ensure that the plan addresses the issues of most concern to the public. There are two ways you can become involved: e 1. ENCOORAGE YOOR MEMBERS '1'0 A'1"1'END '!'BE WORKSHOP ON HAZARDOOS WASTE MANAGEMENT IN YOOR UEA. (See enclosed flyer.) YOO ~Y WISB TO DESIGNATE SOMEONE rROM YOOR ORGANIZATION TO REPRESENT TBE ORGANIZA'1'IpN AT THE WORKSBOP, BOT WE BOPE THAT OTHERS WILL ALSO ATTEND '!'BE WORKSBOP SO '!'BAT '!'BEIR CONCERNS WILL BE HEARD. :2. ARRANGE TO HAVE A SLIDE PRESENTATION ABOOT HAZARDOOS WAST!: MANAGEMENT AT A MEETING or YOOR ORGANIZATION (Call Gloria Anderson at 714-338-4163 to schedule a speaker.) , Public input will make a difference in how hazardous waste is managed in your community. We look forward to meeting members of your organization a~ one of the workshops or at a meeting of your organization. e " e \'-. e e . . CHWMP ADVISORY COMMI1TEE MEMBERS CHARLES BUQUET - city representative. council member. Rancho Cucamonga. County Risk Management. Occupational Health. Safcty Enginecring. former deputy sheriff JOAN DOTSON - public representative, League of Women Voters. Southern California Hazardous Waste Management Authority Citizens Advisory Committee. City of Redla'nds Planning Commissioner, member of San Bernardino County Solid Waste Advisory Council CHRISTINA FERRANTE . environmental representative. Conservation Chair, Los Serra nos Group of the San Gorgonio Chapter of the Sierra Club. Attorney. Member of West End Bar Association PHIL GENTILE, JR. - industry representative. hazardous waste hauler and cleanup contractor. Member of state Household Hazardous Waste Advisory Committee. Officer, Southern California Refuse Disposal Council MICHAEL F. HAYWARD - public representative, Ontario City Policemen. President Inland Empire Chapter Police Officers Research Association of California TOM IRWIN - public representative, Professor of Biology. Victor Valley College. Long-time member of County Environmental Review Board, Desert Conservationist, member of Low-Level Radioactive Waste Disposal Siie Selcction Citizens Advisory Committee, Board of Directors. MOjavc Water Agency. ARDYCE KOOBS - city representative, council member, city of Loma Linda. Member of the Southern California Association of Governments Energy and Envirorrment Committee JIM MULVIHILL - public representative, Professor of Geography and Land Use Planning. CSUSB PEGGY SARTOR - city representative. council member. City of Victorville. Former member of state Hazardous Waste Planning Council. city representative to Southern California Hazardous Waste Authority. Member of Lahontan Regional Water Quality Control Board, former member of San Bernardino County Solid Waste Advisory Council JANET M. WEDER - industry representative. Vice President. Highland Supply Corporation. small quantity hazardous waste generator H-l . . COUNTY OF SAN BERNAIlDINO HAZARDOUS WASTE MANAGEMENT PLAN ADVISORY COMMITTEE e Schedule or Meeti..n ~ , ~tiDIl May 4. 1917 June I. 1917 July 6, 1917 AUlust 31. 1917 October 12, 1917 October 21, 1917 NovelJlber 9, 1917 December 7. 1917 December 14. 1917 January 4, 1988 February 8. 1988 April 18. 1988 May 20, 1988 June 27. 1988 July 6. 1988 July 27. 1988 September 13. 1911 October S. 1988 October 28. 1988 November 11. 1988 December 16, 1988 January 6. 1989 February 3. 1919 February 15. 1989 San Bernardino" San Bernardino Ontario Fontana San Bernardino San Bernardino San Bernardino San Bernardino San Bernardino San Bernardino" San Bernardino San Bernardino San Bernardino San Bernardino San Bernardino San Bernardino San Bernardino San Bernardino San Bernardino San Bernardino Sail Bernardino San Bernardino San Bernardino San Bernardino e · Meetinls between May 1987 and December 14, 1987 focused on consideration of administrative concerns and issues relating to the preparation of the Draft CHWMP. .. Meetinls between January 1988 to February 15. 1989 focused on revisions to the Draft CHWMP based on public and agency comments. These meetincs also considered comments received at the public .hearillgs bef ore city decisioll-lJIakers and the public. e, ..;/ H.2 . . e COUNTY OF SAN BERNARDINO HAZARDOUS WASTE MANAGEMENT PLAN Schedule of Public Worksho~ ~ ~ Locatioll September 2S, 1987 9am to Noon San Bernardino, County Government Center 38S N. Arrowhead Avenue September 29, 1987 9am to Noon Victorville, City Council Chambers 14343 Civic Drive September 30, 1987 7pm to lOpm Fontana, City Council Chambers 83S3 Sierra A venue October 7, 1987 7pm to 10 pm Yucca Valley High School 7600 Sage A venue October 14, 1987 7pm to 10pm Ontario, City Council Chambers e 303 East B Street October IS, 1987 7pm to 10pm Barstow Junior High 1000 Armory Road · The workshops focused on recelYlDg public input on the issues to be addressed in the CHWMP and the Environmental Impact Report. e H.3 . . COMMENTS RECEIVED AT PUBLIC WORKSHOPS - Sail Bernardillo Sentember ~S 1917 Treatment facility location should be close to where waste generated since dumping occurs if disposal is inconvenienL Treatment method and technology should be considered in siting criteria; su bstances being treated should aiso be considered; i.e.. there should be different criteria for different treatment methoc1s. The Plan shouldn't focus on siting criteria alone, that is only part of a total plan of managing materials. Plan should concentra ie on iDventory of existing hazardous waste generation and whether we should permit bringing in more 'problem' materials to this county. The plan should ideDtify those areas where facilities could be located, i.e.. meet certain criteria. There should be different siting criteria for differeDt types of facilities. The Plan should consider the ecoDomic benefits of taking care of waste versus not doina iL ~ Thcre is a need for cooperation between Riverside and San Bernardi~o Counties, e.l.. on groundwater. Vietorville Sentember 29 191'7 What is 'fair share"'! If we take care of our own waste, that should be enough. We shouldn't accept other's waste without financial support. (e.g.. million dollars for roads) Are we measuring the quantity of waste generated? The military now recycles as much waste as possible through the military waste exchange. All hazardous waste handled by the Defense Materials Reutilization Oerice (DRMO). We are trying to recycle and reuse to the extent possible. Problem of collection centers: are people there endangered? Where does it go, where is it treated? Problem is average citizen doesn't know what's toxic, education is necessary. What is the extent of consumer education program? We need to get the word out to reach people. When changing motor oil, the tendency is to dump iL Should pay individually to dispose of it properly. Perhaps have a deposit on oil products. e 8-4 e e ".. ,e " . . Is there a plan to stop dumping of hazardous waste in landfill? What training and certification is available for handlers? Responses from Victorville Fire Department regarding Household Hazardous Waste Collection Center: important that containers arc labelled, oil limited to five gallons at one time, open every Sunday from 9 to 4. Problem of air quality in incineration process, for example the Rialto Tire burning plant. APCD response: Arc now testing for emIssIons in landfill. Haven't evaluated incinerators but there arc control strategies. Risk of incinerators has to be compared with what is coming out of landfills. Off -gassing, causes sickness, landfills being monitored for measurement of fumes, groundwater is also being monitored. Are you measuring Apple Valley landfill on schedule? Are these substances odorless? What about dioxins. Is there communication with other agencies? Docs the permitting authority grant a permit without Environmental Health input? L.A. County Medical Examiner says dioxins arc dangerou1. Science Digest had an article about a town that had water contamination. Is there some connection between landfills and groundwater contamination? The El Mirage tire Shredding plant will affect San Bernardino County. There is a fire potential. We need to stop this proposal. It is dangerou1. I am concerned about the tire shredder and concerned about air quality. Can tires be disposed of by better means? Government should subsidize these operations to prevent problems. Is there monitoring of trains carrying waste? It indicates that the Advisory Committee is considering Groundwater criteria. Is the committee considering more stringent or easier ones? Trying to apply one standard across board may not work, should have different standards for different substances and. different treatment methods. 'FoDtana. Sentember 30 1917 How far are we along in getting people together7 How do you keep facilities out of people's back yards7 What incentives would the county give7 We had a project proposed in Fontana which the people didn't want. There should be new opportunities for people to treat waste locally. San Bernardino County should set the toughest standards for disposal sites. Can we adopt stricter requirements than the federal7 Who decides7 H-S . . I encourale establishment of strict standards to focus attention on San Bernardino County. We should assume leadership for the rest of the states. Are hazardous waste treatment plants Irandfathered in? There is one in Fontana that has been there for 40 years. Who are the eltperts who determine consistency? How do we know the eltistinl plant isn't pollutinl Iroundwater, etc.? - Who appointed the Advisory Committee? What are their qualifieations? If we are successful in attractinl national spotlilht as beinl unattractive to companies producinl "lobbledYlook" we will attract "Iood" industry. This is a larle county with lots of places to dump, such as the desert area. Does the committee plan to be less strinlent and allow facilities to locate here? We should be tryinl 'to promote the idea that CIties take another look at allowinl plants to come so we wouldn't travel Ireat distances to dispose. Who decides. . There should be state fundinl for disposal sites and haulers. lllelal d umpinl occurs because of cost. Is anyth ing beinl considered to reduce costs? Where do the Collection Centers send the household wute? - There should be more emphasis on the three R's mentioned in the slide show, we need to push waste reduction. How many inspectors are. there? And is there enoulh? What is the County number for reportinl illelal disposal? Is this plan leared towards disposal sites or recyclinl facilities? should be s surtalt on refineries for recycling waste oil. It prohibitive DOW. There is cost What is the plan tryinl to do? How much time is allowed? Is it enoulh? We shouldn't put plants near alricultural lands. What about incinerators for municipal wastes? How many tons of hazardous waste are produced in county? Does sny hazardous waste 10 by.rail throulh Fontana? In Canada, our sister city slowed the train to S mph with mounties, could this be considered? How much loes throulh towns now? Should let city know. Will we end up with a plan with Iray areas and loop holes? How can you do a lood enoulh prOlram in the time liven? Will we have to take wastes from outside county? e H.6 , . e e e . . What about military' Department of Defense is a major generator and has problems. How oflen are the military inspected' Are underground tanks safer than above-ground' Will committee address this' Are you compiling concerns of individual cities' How should cities share concerns' What are the statistics on accidents transporting to distant disposal sites' What is difference between your committee and Tanner committee' Could you explain what a local assessment committee is' . What agency regulates hazardous waste facilities' What does the local assessment committee dcal with' Thank you, we learned a lot. Yueca Vane\' October 7 1917 Why didn't we have meeting at County building near library' Current municipal waste disposal is primitive. What about hazardous waste' How well publicized was this meeting' There are a lot of transient trucks in -this area. Nobody knows what's on board. If one overturned at an important intersection we have only one road with no bypass. Such an accident would stop travel to the rest of the area. Are chemical trucks checked' By whom' Do they do any thing bcsides shuffle paper' Joshua Tree dump is identical to some of your pictures. Everything is being dumped there. I am concerned about local landfill. There is no authority to know what is being dumped. No citing authority. Read a letter sent to Supervisor Joyner and his reply. Illegal dumping is being done by residents of outlying areas and other counties. Water will be eontaminated. We need to find out who is dumping and what they're dumping. These problems exist at other landfills also. How long will it be before the plan is in force' Are we following some legiSlation' Will there be hearings in this area' I would like a copy, will one go to the press' The problem of landfills is a cost factor over and above usage fee. Is there a waste disposal site proposed in County' What is the regional authority' When plan comes on line, who will be the enforcement authority' Let's assume a realistic scenario, from 29 Palms to the Marine Base. How is hazardous waste handled' How is it collected' Where is it taken' What are local industries doing with hazardous waste' Dumping' What do H-7 . . photo shops, dry clcancrs do? Looked for a long time to find place to take oil, couldn't find a place. Have called your department about illegal dumping. Some Environmental Healtb people bave been timid in responding. Where can we get help? e Would you come to tbis area with educational programs for generaton? Hope you have a good crystal ball. Environmental rcports are a big waste of money. Rules and regulations are too tigbt. The problem for small businessman is the cost of disposal Must make it easy. People in Moronao Valley very worried about tbe dump site. A lot of stuff dumped that shouldn't be. Ontario Oetober 14 1917 Is the county looking for treatment or disposal facilities somewhere in county? What mechanism will be involved in facilitating siting? Where are two sites currently available? Any proposed sites? Is industry coming forward? Or are they scared off by public reaction? Is there any movement to do labelling of household hazardous waste? Where are collection ccnten? e ::i Is there anything in phone book about hazardous waste sites? Need to know where to take it. Discussion of toxic material left in the ash at the incinerator at Milliken will YOII take care of it? Will it ao to toxic landfill? Is the ash the material that's been scrubbed? Will the burning plant be as clean as tbe one in Germany? Will we be able to aet rid of all the plastic fumes? Barstow. OetobeT IS 1<<}17 How can we be sure that Los Anaeles and Orange County won't piggyback on San Bernardino County facilities? Who's aoing to identify specific site locations for hazardous waste facilities? Unfortunate that committee has only considered siting criteria, would like to see specific sites identified, why this approach? Will county have specific criteria in terms of number of sites? Will they name a specific number? e H-I I I . e e . . Does County have cleanup management plan? Concern about illegal dumpings if responsible party can't be found. This is all going to be handled by private? Does state put out bids? BKK? Problems, hate to see them get in on this. Is City of Barstow going to encourage waste facilities? How dangerous will these toxic wastes be? How do we measure? Would mercury be as dangerous as it was in its original form after trea tmen t? Until state sets guidelines. we won't know how dangerous material wiIl be? Is anyone considering incineration unit in this area? How about spent solvents and heavy industrial incinerators? H-9 . . COUNTY OF SAN BERNAIlDINO HAZARDOUS WASTE MANAGEMENT PLAN e t Sehedule or Puhlie Hearhlu Oft the nnrt C'HWMP ~ :I:.ia February 24, 19&& 7:00 PM. March 16, 19&& 1:30 PM. Mareh 21, 19&&, 7:00 PM. March 30, 19&8 7:00 PM. H-I0 Loc:atiOD San Bernardino County Museum 2024 Oranle Tree Lane Rcdlancb San Bernardino County Government Center. 3&5 N. Arrowhead Avenue San Bernardino Alta Loma High Sehool &880 Baseline Road Rancho Cucamonga Yictorville City Hall Council Chambers 14343 Civie Drive Y ictorville e . ) e e \ e e . . COUNTY OF SAN BERNARDINO HAZARDOUS WASTE MANAGEMENT PLAN Schedule or Public HeariD2s on tbe Dnlrt CHWMP Before City DecisioD..Maken ~ :Iim Location January 26, 1988 2:00 P.M City of Redlands. Planning Commission February 1,1988 7:00 P.M City of Chino, Planning Commission February 2, 1988 7:00 P.M . City of San -Bernardino, Planning Commission February 3. 1988 6:00 P.M City of Big Bear City Council February 8. 1988 7:30 P.M City of Fontana, Planning Commission February 9, 1988 6:00 P.M City of Rialto, Planning Commission February 9. 1988 7:00 P.M City of Twentynine PiJms, City Council February 15. 1988 12 Noon City of San Bernardino. City Council February 16. 1988 3:00 P.M City of Highland, City Council February 16, 1988 6:00 P.M City of Rialto. City Council February 16. 1988 6:00 P.M City of Rancho Cucamonga City Council/Planning Commission February 22, 1988 7:00 P.M City of Fontana. Planning Commission February 22, 1988 7:00 P~M City of Victorville CityCouneil/PlanningCommission February 23. 1988 5:00 P.M City of Loma Linda, City Council February 23, 1988 7:00 P.M City of Adelanto, City Council H.II . . e APPENDIX I HAZARDOUS MA TERIAL/W ASTE INFORMA nON DIRECTORY e e e e e . . APPENDIX 1 HAZARDOUS MATERIALS WASTE INFORMATION DIRECTORY This directory provides the phone numbers of a few resources available to businesses and the public for information and assistance on hazardous materials and hazardous waste issues. The list is by no means exhaustive but provides initial contacts to assist in obtaining information and additional references in several topic areas. The directory begins with emergency phone numbers and then is arranged alphabetically according to the following categories. fiG. EMERGENCIES 1-2 Complaints 1-3 1.3 1-4 Community Right to Know Household Hazardous Waste Laws. Regulations. and Permits 1-4 Reporting Hazardous Materials/Waste Incidents I-I] Training 1-12 Waste Disposal/Reduction/Recycling 1.12 Workplace Hazards 1-13 1.1 . . EMERGENCIES e F or assistance: Sberirr. Police, Fire, Environmental Health Includinll Hazardous Materials Response Units 911 For hazardous materials information: ChemTrec (Chemical Transportation Emergency Center) 100/333-3360 Poison Control Center 714/294-6000 County of San Bernardino. DEHS 714/317-3044 Hazardous Materials Division If the incident involves hazardous discharge or threatened discharge to drains. gutters. sewers. etc.. contact: County of San Bernardino. DEHS. Hazardous Materials Division Field Services 714/387.3010 Hu-Mat Team 714/317-3044 e , / County of San Bernardino. DEHS. Interagency Hazardous Materials Response Team (24hrs) 100/33-TOXICS After immediate assistance has been summoned. or if no outside assistance is necessary. you may have a legal responsibility if you were involved in the incident. or are an employee of the responsible party. to notify these agencies: (see also REPORTING INCIDENTS. page 1-11) County of San Bernardino. Environmental Health Services, 714/317-3044 Huardous Materials Division. Hu-Mat Team/Right to Know Office of Emergency Services. California National Response Center 100/852-7550 100/424.8802 e 1-2 e e e . COMPLAINTS . To report any nuisance, harmrul, suspicious, or illegal activities relating to hazardous materials or hazardous waste: (anonymous calls accepted) County or San Bcrnardino. Environmental Healtb Servic:ca, Hazardous Matcrials Division Haz-Mat Team Field Services Toxies Hotline State or California, DcpL or Health Services, T.5. Central Division Los Angeles Orfice Long Beach Orfice 714/3g7-3044 714/387-3080 IOO/33-TOXICS 213/620-23g0 213/590-5950 Soccial Circumstances: ror these types or complaints, please contact the listed agency: Air Pollution South Coast Air Quality Management District (AQMD) Colton Orfice EI Monte Orfice County or San Bernardino, Air Pollution Control District (APCD) Desert Consumer Products Consumer Product Sarety Commission 714/g77-1444 818/572-6200 619/243-8147 100/638-2772 213/688-7273 Pcsticide Use and Disposal County-or San Bernardino, Agricultural Commissioner's Orfice 714/387-2120 Workplace Hazards Public Sector Employees: Cal OSHA (local and state gov'ts) Private Sector Employees: Fed OSHA (and rederal gov't employees) COMMUNITY RIGHT TO KNOW 818/901-5403 7141383-4321 213/514-63g7 818/915-1558 800/648-1003 To obtain inrormation regarding hazardous materials at a particular racility, submit a written request by mail or in person to: County or San Bernardino, Environmental Health Services, Hazardous Materials Division 385 N. Arrowhead Ave. San Bernardino, Ca. 92415 1-3 714/317-3044 . . Up to 10 days may be required for staff to prepare the file for public: review. Trade secrets, confidential information, and specific locations of materials will not be disclosed. A fee may be charged for this service. For regional information contact: . Region I Local Emergency Planning Committee Office of Emergency Services 107 S. Broadway, Room 19 Los Angeles, Ca. 90012 213 / 62()' 5607 100/&52-7550 HOUSEHOLD HAZARDOUS WASTE For information regarding safe use and disposal of household hazardous waste, contact: County of San Bernardino, DEHS. HHW Program 7141317-4629 LAws. REGULATIONS, AND PERMITS LOCAL: ,San Bernardino County aDd Incorporated Cities County of San Bernardino Environmental Health Services, Hazardous Materials Division 714/317-3010 714/317-4629 714/317.3044 e ',' Lead agency for hazardous waste, underground tanks, community right to know/emergency planning laws, infectious waste, site mitigation, radiological health, epidemiology, toxicology and household hazardous waste in all areas of the county. County of San Bernardino, DEHS Tanner Program 714/317-4629 Hazardous Waste Management Plan implementation and information regarding permitting of specified hazardous waste facilities. County of San Bernardino Agricultural Commissioners Office Regulation of pesticide use and disposal in all areas .of the county 714/317.2120 County of San Bernardino Air Pollution Control District (APCD) Air quality and emissions regulations, Desert Region 619/243.1147 South Coast Air Quality Management District (AQMD) Air quality and emissions regulations, Mountain and Valley Region Colton 714/177.1444 EI Monte 111/572-6200 , .....:<,. 1-4 e e e . . FIRE DEPARTMENTS: County Areas aDd Incorporated Cities San Bernardino County Forestry and Fire Warden Department Adelanto FD P.O. Box 10 Adelanto 92301 Acrojel Ord. Co. Rl. 4, Box 454-E Chino 91710 Apple Vaney FPD 12143 Kiowa Rd. Apple Valley 92308 Arrowbear Lake CWO Box 45 Arrowbear Lake 92308. Baker FD P.O. Box 186 Baker 92309 Barstow FPD 861 Barstow Rd. Barstow 92311 Big Bear City CSD P.O. Box 558 Big Bear City 92314 Big Bear Lake FPD P.O. Box 2800 Big Bear Lake 92315 Calif. InsL for Women 16756 Chino-Corona Rd. Frontera 91720 CDF 3800 Sierra Way San Bernardino 92405 Center FD P.O. Box X-4 MCAGCC 29 Palms 92278 Central Vaney FPD P.O. Box 1040 Fontana 92335 714/387-4212 (619) 246-8606 (714) 528-7281 (619) 247~7618 (714) 867-2704 (619) 733-4402 (619) 256-2254 (714) 585-2565 (714) 866-7566 (714) 597-1771 (714) 882-1226 (619) 368-6871 (619) 829-1441 1-5 e e e . . George Fire/Crash Sta 35 Civ. Eng./Der. George AFB 92392 Grand Terrace FD (714) 882-1226 3800 Sierra Way San Bernardino 92405 (619) 269.2241 GreeD Val. Lk CSA-79 FD (714) 867.2176 P.O. Box 241 Green Valley Lk. 92341 Hesperia FPD (619) 244.9000 17288 Olive St. Hesperia 92345 Joshua Tree FPD (714) 882-1226 3800 Sierra Way San Bernardino 92405 K.aiser Steel FD (714)829-3332 P.O. Box 217 Fontana 92335 K.err-McGee Chem Co. P.O. Box 367 Trona 93562 (619) 372.4311 Lake Arrowhead FPD Box 130 Lake Arrowhead 92352 (714) 337.8586 Landers VFD 3800 Sierra Way San Bernardino 92405 (714) 882-1226 Loma Linda FD 11325 Lorna Linda Dr. Lorna Linda 92354 (714) 796-0191 Lucerne Valley FPD Star Route 3868 Lucerne Valley 92356 (619) 248.7322 Lytle Creek Cyo OFC 3800 Sierra Way San Bernardino 92405 (714) 882-1226 MODtclair FD Box 2308 Montclair 91763 (714) 626-1217 1-7 . Monte Vista FPD P.O. Box 2308 Montclair 91763 Moron go Valley CSD 3800 Sierra Way San Bernardino 92405 Mt Baldy FD P.O. Box 483 ML Baldy Mt Pass VFD Moly Mine Mt. Pass 92366 Nat'l Grd Tmg Ctr FD US Army Fort Irwin 92310 Needles FD 3800 Sierra Way San Bernardino 92405 Newberry Springs CSD Box 206 Newberry Springs. 92365 Norton AFB 63 ABG.DEF Norton AFB 92409 Ontario "FD 425 East B St. Ontario 91764 Ontario Airport FD Ontario Airport Ontario 91761 Parker Dam VFD U.S. Bureau of Reclamation Parker Dam 92267 Redlands FD 525 E. Citrus Ave. Redlands 92373 Rialto FD 131 S. Willow Ave. Rialto 92376 . (714) 626-1217 . (714) 8&2.1226 (714) 982.1213 (619) 856-2201 (619) 386-3497 (714) 8&2-1226 (619) 257.3316 e /:j (714) 382-7234 (714) 986-4579 (714) 984.1207 (619) 663.3712 (714) 798.7600 (714) &20-2501 - 1.& . . LAWS. REGULATIONS. AND PERMITS (continued) e .., STATE Department of Health Servicc:s, Toxic Substance Control Division Alternative Technology 916/324-1789 916/322-2337 916/324-1781 415/974-7473 916/324-1807 916/324-3773 Public Information Legislation, Regulations EPA Numbcrs Program Mgmt. Section Ofncc of Emersency Services State agency for community right to know/ emersency planning laws 800/852-7550 LeSislation 916/427-4287 916/427-4542 tt Hazardous Materials Division Health and Welfare Asene)' Lead aseney for Proposition 65, the Safe Drinking Water and Toxic Enforccment Act 916/445-6900 u.s. Government Bookstore (copies of CFR 40/49) Ofnce of Permit Assistance 213/894-5841 916/322-4245 Resional Water Quality Control Board Santa Ana Resion Lahontan Region Colorado River Basin Resion 714/787-4130 619/241-6583 619/346-7491 FEDERAL Environmental Protection Asency Generallnformlltion Toxic Substance Division 415/974-8071 415/974-7422 -" 1-10 . . e Small Business Ombudsman 800/368.5&&8 RCRA &. CERCLA 800/424-9346 TSCA 800/424-9065 Asbestos 800/334-8571 Radon 800/334-8571 PCB's 415/974-8071 Business Assistancc 415/974.7472 e e REPORTING HAZ.ARDOUS MATERIALS/WASTE INCIDENTS If emergency response or immediate assistance is rCQuired, dial 911 and refer to EMERGENCIES, page 1-2. . To report suspicious hazardous matcrials/waste activities, see COMPLAINTS, page 1.3. If you or your business are involved in a release or threatened release of a hazardous material or hazardous waste, you are required by law to notify the following agencies within 24 hours of occurance, even if the ineident dt)e~ not warrant emerl!enev re~nonse I:~Sist8nee. County of San Bernardino, Environmental Health Services, Hazardous Materials Division 714/387.3044 Office of Emergency Services. California 800/852-7550 Dcpcnding on the type and severity of the incident. additional agencies may need to be contacted. For examDlc: Environmental Protection Agency 415/974-8153 213/590-5132 800/424-8802 Department of Fish and Game National Response Center Regional Water Quality Control Board Santa Ana Region Lahontan Region Colorado River Basin Region 714/787-4130 619/241-6583 619/346-7491 I-I J -. . TRAINING e Information and training programs for hazardous materials/waste management: California Highway Patrol 213/736-2981 a three phase training course for hazardous waste identification, clean up, recovery, and emergency response California Specialized Training Institute, San Luis Obispo Courses for emergency response personnel for government and industry 805/544-7102 UC Extension, Riverside 714/787-5804 12 week courses on hazardous materials management, a 2 year certificate program, and one day seminars and workshops WASTE DISPOSAL/REDUCTION/RECYCLING For small quantities, sce also HOUSEHOLD HAZARDOUS WASTE: ~ For general information and assistllncc; or to find a service station or auto repair shop that will except small quantities of waste oil: County of San Bernardino, Environmenta] Health Services, Hazardous Materials Division Provides IiSlS of companies, services and disposal sites Field Services Household Hazardous Waste 714/387-3080 714/3g7-4629 For recycling information, inCluding waste oil: California Wasle Management Board, Recycling Hotline 800/952-5545 For assistance with waSle disposal alternatives; waste reduction projects; or for a list of commercial recyclers and businesses offering or needing waste for re.use: Department of Health Services, Alternative Technology 916/324-1807 California Waste Exchange e ./. 1-12 e e e . . WORKPLACE HAZARDS For inrormation on hazards in the workplace: Cal OSHA Consultation services 213/861-9993 For complaints and inspection requests: Public Sector Employees: Cal OSHA (local" State gov'ts) 7141383-432] 818/901-5403 Private Sector Employees: Fed OSHA (rederal gov'l employees) 800/648-1003 213/5]4-6387 818/915-1558 1-13 . e APPENDIX J COMMENTS RECEIVED ON DRAFT CHWMP AND RESPONSE TO COMMENTS e A separate documcnt available through the Departmcnt of Environmental Health Services 3B5 North Arrowhcad San Bernardino. Ca. 92415 e . ~ . , . e " 14.g50'.oOO ~;NUTLS OF THE BOARD OF SUtRVISORS OF SAN BERNARDINO COUNTY. CALIFORNIA EHS-Gen. EHS-Hazardous Waste S.C. Haz. Waste Mgmt. Auth. .January 22, 1990 FROM: PAUL F. RYAN, Director Department of Environmental Health Services SUBJECT: 'rRE ADDITION OF FAIR SEARE LANGUAGE TO '1'EE APPENDU OF 'rRE COUNTY'S JlAZARDOUS WASTE KANAGEHEN'l' PLAN RECOMMENDATION: Adopt Fair Share Language into Appendix of Hazardous Waste Management Plan BACKGROUND: The Fair Share Language was the result of a cooperative effort between the Chairman of the Board of supervisors in her capacity as the Chair of the Southern California Hazardous Waste Management Authority, and the Director of the State Department of Health Services. The State Department of Health Services has required that this language be incorporated into the San Bernardino county Hazardous Waste Management Plan prior to State approval of the plan. The result is greater local control over the siting of hazardous waste facilities. REASON FOR RECOMMENDATION: Addition of this Fair Share language is needed prior to final approval by the State. REVIEW BY OTHERS: Susan Nash, County Counsel, on January 17, 1990. FINANCIAL IMPACT: No financial impact expected to result from this addition. PRESENTER: Peter Brierty cc: EHS-Brierty -State Dept. of Health Services c/o ms EPWA File Action of the ,Board of Supervisors ~""";\\'\\IIIII' .~" ~~ SUPE!~!, III/ APPRrnf~'6'BP..iRD'6F:i~~ERv'SORS CO~'Ii" 'Q"'. .~S" 'N':.Bt:RN~~INO ~ I'!;''). ........:.~.,. . __ ~ ::: en. ...~;: ". .~"~;~ ~ . ~ ~ Absent ','OTION Se~~ , .~.'.f ~!: :~ _, IY' 7.' _ . . .,' ~ ~"'''' . '" -4 5 lZ ';\.... '1-~"f"tt~\~~" ~ ;: EARLENE SPRO~ ~ ~~~~ {q~'~~E ~?"if:ff BY ~t . QI\\\\\\"'" DATED: ITEM-.l5 cD r~ . . I: e--Uooo....~_.,..... ....~ ,"",'.U .~,,=- . ,RTMENT OF HEALTH SERVICES ; .uf:" , S':'l(["1 o ":>1 U::'): ..~""'Q. 'to .,:~,~,~ (916) US.H~B ~:-E Clf;.llUt:J:...... c---.. ~ OctobH 6. 19~, 10: Le.~ A;encies Pre~.ring County and Regiona' H.z.rOo~s ~.sta ~lnagEment Plans SUS:~Ci: C0~IS;V fi~.!~.~JJ::S \i.!.S1~ "',:''i~.~~!'.E'''T PLASS It has co~e to ~y atte~ticn that there continues to be considerable concern, and perhaps ~isunderstanoin~, abo~t this Department's position regarding "fair _ share" lir;,itatiol\s contair.ed in the county hazardous wast.e Ir.anagelr,ent plans ~mancated by AS 25'S (1;:5), and 1 would li~e to t.ry t.o clarify t.he issue here. Given t.hat these plans will ultimately form the basis for California's capacity to handle hazardous waste. the Department has consist.ent.ly expressed its concern that unconditional "fair share" limitat.ions potentially could crute inadeq"ate state\<iice hHardous waste capacity. Thus, as has been stated in previous communications from t.he Toxics Substances Cont.rol Division, unconditional 'fair share" limitat.ions on facility capacity In any county plan would be judged inconsistent ",ith t.he Department's guidelines for preparing these plans and, thus, grounds for disapproval. However, the Department has also recognized t.he validity of each local jurisdiction's need to provide its residents with sor.:e de;ree of assunnce t.hat. t.heir jurisdiction would not beco~e unfairly targeted as a receiver of the State's hazardous waste. Indeed, in recognition of these needs, the Department issued 'ett.ers on April 13 and December 27, 1988 describing parameters under which conditional 'fair share" lilr,itations would be acceptable in t county plan. Nonetheless, we understlnd that there continues to be some confusion about these conditions and, particularly, with regard to who bears t.he burden of proof. Pursuant to a ~eetin9 earlier t.his week wlt.h representatives of severa' local jurlsdlct.lons, 1 wanted to tal:.e this opportunity to clarify SOlfle potent ill zlsunderstandings t.hat were voiced at t.he ~eting, as well as to elaborate on the conditions under 'lthich the Oepartsent .Ight accept "fair share" 1\...ihtions in a cou~ty hazardous 'ltut.e canageMnt plan. SpecifICa'1y, the Oeplrtlllent would likely accept 'faIr share" 'ialhtions in count)' huardous e waste Eanlgement plans if they were condItioned upon :he following concepts. ,. Approval of proposed hlzardous Wlste I\lnagement fac'1'ties that do not exceed l jurisdiction's "fair share" will depend on siting crtteril only. . . e Page 2 Oc tober 6. 19S9 2, [ffHtlve in'tI'cOllntY/T~qi(lnal agrec",~nts maybe u~erl to rpach a jurisdiction's "fair share" re$ponslbillly. 3. ^ county can reject a IH'oposed hazArdous waste m~na\lp.ment. facility/proJect that exceeds its "fair sharp," If l.here "Ie errectl...e InterJurlsdicllon~l (Intcrgtlvornmental/reglonal) agreemcnt(s) for transrH of the county's haurt;lous wastes. ~. If effective InterJuri$dlctlonal agreements do not exist. a juri~dlctlon shall not reject hara,'d<:>us WBte manageftlent. prtlposals t.hat exceed "fall' share' If the rroron~nt d~",onstrAtes that the "faIr share" (l.e,. s",~ller) facIlity i$ ecC\nomlcallY non-viable, exc@pt In cases In whlc.h the jur.lsdlction Ol.'ftlonstratB that there l\l"'l appreciably Increased publiC heal th ~ll\l/or envlrlJTunental rlsk.s assc>clated wlt.h the ~,roposl.'d (\.e.,hrger) 'aeilHy, Thl.' last ro1nt may wal','ant. some funher exphnation, Undel'stanr.lably. a local jurisdictIon nllY h~vp. legitimate concern about siting hatardolls wast'! manngomont facll ILles larger then needed to handle Its .'air share" because or pot~l1tlally Id\lher "\sks to the. 'local co"",unlty associated wllh the laT9et" faelll\.y. And whIle! the Dp.pat.tm!nt has always felt. t.hat t.he CEQ,~ ;.,,(1 varIous permlltll19 processes would adllquately provide protectlons In litis regard. based on lhe COn(:p.l"nS expresser! to us by counties In recent month~, I believe that we could Ie-cept a phil that. allows 1I local Jurlstllcllon to dlnpprove proposed facilities that exceed 1I Jurlsdlcllon'S hatardolls waste management n~!ds If It den\onstntes that th~t'e .\"e apl't"p.clably Incr-eased pullllc health and/ol' onvl,'onntcnhl associated wIth the larger facility. I \'ec~gniH that tho Information pt'ovldl!d in this nntlce cumes lale in Ih'! rhnnlng process. but. TlOMtheless. we f'l1t that ~Ienef)ded to nlake one nlore effort. to try to 'lnsun that a full understandlnll of ollr posHlon exIsts so that modlflcallon of local plans 'Cln bl! achieved', If your "nal plan has .lre:ld)' l;1een submlL\.ed to the Department and you wish to modify It to Inclode t.he above concepts. phase notify All!x R. Cunnlnyham, Chief Oeputy [Ilt'ector rOI' Iho Toxlcs substances Control Olvlslon, as soon as posslbh, Thl! Itullflcallon needs to'be In wrl\.lny and rocelvodby \.he Op.partment. no latH lhan /lovember " 1909. Lanyulye" such as specified abov!! could be eUOy subst.ltuted In YOU1. plan If you so dull'e. If )'OU have any questions, please 00 not. hultat!! .t.o contact 1ft'! or !'Ir. Cunningham. e e (~.~~ Kenneth W. Kizer, H.O.. Olrector - H.r.lI. cc: Se9 nexl page .. e e . . : ~y~u OF LAND MANAGEMENT l1i.~~ CALIFORNIA DESERT DISTRICT 169S Spruce _ Ri>cnidc. CoJjlomia 92507 Mr. Michael K. Lerch Land Management Department Environmental Public Works Agency 385 North Arrowhead Avenue San Bernardino, CA 92415-0180 Dear Mr. Lerch: IN Uft.t' UJ'D TO: 1786 (CA-068.20) MAR 1 0 1989 The enclosed Memorandum of Understanding (MOU), concerning specified hazardous waste facilities on or near public lands, between San Bernardino County and the Bureau of Land Management is ready for signature. This version of the MOU incorparates all of the revisions which you previously suggested. In many respects, it simply defines the cooperative manner in which we have been working for many years. If this document is acceptable to the County, have the attached 3 copies of the MOU signed by the Chairman of the Board of Supervisors. Please then return 2 copies back to this office. Should additonal changes be necessary, please contact Wes Chambers at (714) 351-6402. We will make the necessary corrections and return the copies for County signature. Sincerely, AHJ I{::,e/- - .Gerald E. Hillier ACTING District Manager Enclosure . . FO~CO . YI.:SEO~LY C:I..""y ~.:..r~~I\' COl":~.';1 "'.~:'.r Environmental Health Services Co..n~,. :>.~.rtr".n, CO"'''';~ .....'...nt.'.... 90-157 CDI\Ue:UH', L,.;'nle !\:...I"I'I:,... \ \,1,1' -r&\ COUNTY OF SAN BERNARDINO ~~/~'~~'" CONTRACT TRANSMITT AL /11111\ ?am Bennett ~f\. E-..t. 4692 ."';>>,., U'h' No. Swc..OClo,'C.t 1'\,;0. .lo~ "D. I.,I'T'.o",r.t o! CO~tl': 631 -0- "'o;"Ct Na"'.: /'lOU Concerning Hazard- ous Waste Facilities If connect h., ""0" ,t-..,. on, ~'Y'rn.nt or ,t:.;~ co",plet. ,,,. 10Ilcowj"l: ".,......",. Enirn.,,: ADpfoairr:", A""o",", E.,.,: Contractor: Bureau of Land Management Birth Date Federal I D No. or Social Security No. Contractor's Representative: John Key, Bureau of Land Management Address: 1695 Spruce Ave, Riverside, CA 92507-2497 Phone: 7141276-6402 ex... 'i.L. Nature of Contract: (Sri!fly d,scrib, rn, g!Mfll r,rms of rh, corm.:r,1 e The Memorandum of Understanding (MOU) is between the United states Bureau of Land Xanagement and the San Bernardino 'County Department of Environmental Health Services. Intermingled public and private land ownership patterns necessitate the cooperation of federal, state and local land management agencies in processing of applications for Specified .Hazardous Waste Facilities (SHWF). The goal of this MOU. is to. establish a cooperative effort for proper review and 'processing of SHWF's applications in an efficient and non-dupl~cative manner. ~ _. " ,- . f J ...... fr.ch rhis tranJmiff" fo.1/ contracf' nof p,.p.,.d on rho "Sf.nd.rd Contr.c," form.} weel ., ,. L.p' 'erm ; 6w~ L-. tVll-~ Cownty Co"",., Do'. l - .l.::?r - ~ Rev....d ., '0 Affirlftllt'" Ac,io" ".",ihW.d for ",oc.uiftl ~#~. - .5 . ~ A.e,..:y AClmiftilv".,/CAO Dat. I-I 7~O Dot. 02.'n....ooo...... '.'11 e e ~ : . . MEMORANDUM OF UNDERSTANDING BE~.tEN THE CALIFORNIA DESERT DISTRICT OF THE BUREAU OF LAND MANAGEMENT AND THE COUNTY OF SAN BERNARDINO ON COORDINATION OF PER~ITTING PROCESSES FOR SPECIFIED HAZARDOUS WASTE FACILITIES ON/OR NEAR PUBLIC LANDS INTRODUCTION AND PURPOSE: Intermingled public and private lando,mership patterns necessitate the cooperation of federal, state and local land managernent agencies in processing of applications for Specified Hazardous Waste Facilities (SHWFs) in the California Desert. The goal of this cooperation is to provide for proper review and processing of SHWFs applications in an efficient and non-duplicative manner. The Burea~ of Land Management (B~~) must comply with the Federal Land Policy and Management Act of 1976, the Mining Law of 1872, the Endangered Species Act, the Wilderness Act, and other legislation as to the use of public lands for SHWFs. Both agencies agree that SHWFs should be reviewed, evaluated, and permitted systematically, in accordance with Chapter 1504 of the California Health and Safety Code and County Hazardous waste Management Plan (CHWMP) and that review should be coordinated between the affected land management agencies. The purpose of this agreement is to define the expected w9rking relationship between the BLM and the County of San Bernardino and to establish mutually acceptable procedures for processing SHWF applications proposed for location on, or adjacent to, public lands in the California Desert. AGREEMENT: Both oarties of this MOU acree: 1. that the County will be designated as lead agency for all SHWF applications; 2. that the review processes and procedures specified in california Health and Safety Code (Chapter 1504), in the County Development Code, and in the General Plan and that the necessary review and conveyance procedures set forth by BLM policy and regulation will be jointly used; that, when approached with a proposal for a SHWF, the permitting agencies will hold a joint pre-application conference to inform the applicant about locations which are subject to constraints based on land use guidelines and the CHWMP pursuant to California Health and Safety Code (Chapter 1504); 3. e e e . . BLM/COUNTY NOU SPECIFIED HAZARDOUS WASTE FACILITIES Page 2 4. that copies of maps, permit applications, ana other submittea information receiv.ea by one agency will be proviaea to the other agency ana that application review will be coordinatea bet",'een the County Lana Management Department, the County Environmental Health Services Department, ana the applicable BU~ Resource area Office(s) (Neeales Resource Area, Barstow Resource Area, or Riagec~est Resource Area); 5. that appropriate environmental review will be jointly undertaken meeting each agency's California Environmental Quality Act and National Environmental Policy Act requirements; 6. that each agency will consider the policies of the other with respect to aemonstratea neea for any SHWF; that waste disposal facilities cannot be located on BLM administered public lanas without first transferring such lana out of BLM ownership in conformance with applicable BLM planning procedures and policy; 8. that the applicant for a SHWF does not need to acquire public lanas prior to application but must obtain in writing a determination from the BLM Authorizea Officer (Neeales Resource Area, Barsto~ Resource Area, or Riagecrest Resource Area) that the lands are available, subject to the finaings of 'an environmental analysis, for transfer out of public ownership through sale or exchange; 7. 9. that the applicable BLM Resource Area Office will screen any related proposed public lana acquisition or authorization for suitability/availability in a tilnely fashion so as not to hinder filing of the SHWF application. The BLM furthermore agrees to inform the applicant and the County at that time of the basic conditions for such a sale or exchange; 10. that the County as the lead agency will process the SHWF proposal as a whole--incluaing not only the site approval but depenaent actions such as authorizations for access routes, and power lines--and will issue no permit or site approval without a parallel decision made by the BLM to transfer the subject land or issue other appropriate lana use authorizations; .. '. . e e e - . . B!.!-i;COUNTY MOO SPECIFIED HAZARDOUS WASTE FACILITIES page J 11. that the BLM will process such exchanges or sales in a timely manner subject to fiscal constraints and pertinent laws and regulations: 12. and that, prior to and after adoption of a CHI\'MP, all provisions of this MOU will be followed. This agreement may be terminated by either party upon thirty (30) days written notice to the other party. ..3//t/ / 'i'? Date ' I YN~~~~~~. - Gerald E. lier ACTIN~ District Manager ~ California Desert District Bureau of Land Management FEB 0 5 1990 ~~ ~~. E Barbara Rior an - Chairwoman, Board of Supervisors San Bernardino County California Date ", ". ~- , , -. ..." . .....-. .. , , . - ", " ....: .". .,c.:.."-...... ..... ", ..,:' '. i.' .-:. .~. :' : . '. ..;~ ....-.':"'.--: .,'"