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Appendices
Appendix ] Facility Plan
General Plan Update and AJSociated Specific Plam EIR
The Planning Center
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Appendices
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Genera! Plan Update and Associated Specific Plam EIR
The Planning Center
DOMESTIC WATER, IRRIGATION WATER
W ASTEW A TER AND RECYCLED WATER
FACILITY PLAN
ARROWHEAD SPRINGS PROPERTY
AUGUST, 2004
Revised: 5/12/2005
Prepared For:
AMERICAN DEVELOPMENT GROUP, INC.
24600 ARROWHEAD SPRINGS ROAD
SAN BERNARDINO, CA 92414
(909) 875-1400
Consulting Services
J-l
TABLE OF CONTENTS
Description
Section 1
Introduction
Section 2
Study Area
Section 3
Domestic Water
3.0 I-General
3.02-Water System Design Criteria
3.03-Water Source
3.04- Domestic Water Requirements
3.0S-Project Phasing
3.06-Domestic Water Pressure Zones
3.07-Water Source Requirements
3.08-Reservoir Sizing
3.09-Water Treatment
3.10- Watee Distribution
Section 4
Wastewater
4.0 l-General
4.02-Wastewater Quantities
4.03-Wastewater Collection System
4.04- Wastewater Treatment
Wastewater Loadings
Effluent Requirements For Spray Irrigation
Wastewater Treatment Process and Redundancy
4.05-Wastewater Collection
4.06-Permitting
Section 5
Irrigation Water
5.0 l-General
5.02-Irrigation Requirements
5.03-Irrigation Water Source
5.04-lrrigation Water Distribution
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Page
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7
9
9
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10
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15
17
20
22
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27
27
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29
30
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33
35
35
38
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41
42
PLATES
Description Page
Plate 1-1: Location Map 6
Plate 2-1: Study Area 8
Plate 3-1: Proposed Land Use 12
Plate 3-2: Project Phasing 14
Plate 3-3: Hydraulic Schematic 16
Plate 3-4: Ultimate Water System 24
Plate 3-5: Preliminary Surface Water Treatment
System- Coldwater Creek 25
Plate 3-6: P~liminary Surface Water Treatment
System- Strawberry Creek 26
Plate 4-1: Ultimate Wastewater Collection System
And Proposed Treatment Plant Location 32
Plate 4-2: Schematic Flow Diagram- Wastewater
Treatment Plant 37
Plate 5-1: Absorption Schedule 44
Plate 5-2: Backbone Irrigation System 45
3
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SECTION 1
INTRODUCTION
The historic Arrowhead Springs Hotel and surrounding properties are planned for
development t!trough a Specific Plan to be processed through the City of San Bernardino
as a policy document or regulatory document for the City to use as a guide for the
development. The Arrowhead Springs Hotel and surrounding 1,916 acres of property is
under o\Wership of the Campus Crusade for Christ. TIlls hotel and properties was once
the headquarters of the Campus Crusade for Christ prior to moving to Florida.
The water resources of the area include hot and cold springs, surface streams and
groundwater. The hot springs known to the mission fathers as "Aqua Caliente" (hot
water) and was to be believed to have healing qualities. This is recorded in a letter from
Fray Zalvida in 1820 to a fellow priest that Fr. Jouquin (Nuez) "C{)ntinues troubled with
his diseases, and today (Sunday) he was unable to say Holy Mass. He is thinking of
going, in a short time, to the sierras in order to take the baths of Aqua Caliente; he will
stay there at least 15 days." In 1857, Dr. David Noble Smith along with John Brown
developed the springs and created the Spa at Arrowhead Springs in 1863 also known as a
Hygienic Sanitarium.
The first Arrowhead Hotel was built by David Noble Smith aroWld 1868, and Messrs.
Darby and Lyman of Los Angeles, who had been leasing the Hotel from Dr. Smith, built
the second Arrowhead Springs Hotel in 1885. This beautiful wooden structure was the
largest hostelry in San Bernardino Cotmty. A third Arrowhead Springs Hotel was
constructed in 1905, by San Bernardino businessman Seth Marshall and he started
bottling "Arrowhead Springs Water", actually water from Waterman Creek, to supply
customers in southern California and Arizona. In 1930, the water supply changed from
Waterman Creek to springs at the 5300-foot level in Strawberry Creek to upgrade the
changing water quality in Waterman Creek due to the development ufhomes nearby.
In 1939, a new concrete hotel was constructed and after a number of owners, it was sold
to Campus Crusade For Christ in 1962 and they still own the hotel and property at the
present time.
The naturally formed Arrowhead on the mountainside northerly of the hotel has withstood
many fires and in 1957, the United States National Forest Service designated the natura!
Arrowhead a "Landmark Geological Area."
During the periods of the hotel ownerships and Campus Crusade For Christ, the water
resources have been expanded and restored and are in operation as of today. These
resources will play an active part in the water supply for the proposed development. The
water supply will include drinking water for domestic uses and non-potable irrigation
water for landscape maintenance and aquatic features such a lakes, fountains and other
4
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types.
The development, which will utilize about 506 acres of the 1916 acres of the ownership,
will require the generated wastewater to be treated to a degree whereby effluent will be
available for unrestricted use. These uses will allow the community to be "water-wise",
self-contained.
This facility planning document will estimate the quantity of water required for both
domestic and irrigation water use, the amount of wastewater generated and the use of the
treated wastewater. Upon obtaining the quantities of water needed for each specific use,
the water source will be identified. The type of wastewater treatment will be utilized and
the "fail safe" facilities identified will be discussed and the location of the units
determined.
The distribution of the domestic water will be described with potential water pressure
zones identified with sizing the distribution reservoirs and estimates for fire suppression
included. Booster stations with pumping capacity and redundant facilities will be
detennined. If surface water or certain springs are used, the use of treatment prior to
domestic use will be discussed along with the type of treatment and shown on the
appropriate plates herein.
The irrigation water facilities will be identified and the use of stream flows in conjunction
with recycled water from the wastewater plant will be determined. A backbone system of
the irrigation water sources, distribution system and pumping facilities along with
capacities will be identified.
This report provides a comprehensive document for developing the water resources and
the facilities to transport the water to the areas of proposed use as defined within the
Specific Plan. The utilization of the recycled water from a wastewater treatment plant will
be shown for a self-contained system for the Arrowhead Springs Specific Plan of
development.
Alternative water supply sources and wastewater services win be discussed with the City
of San Bernardino being an alternate provider to the on-development of wet-utilities. The
alternate sources will be described and a preliminary "Opinion of Probable Construction
Costs" shown for each alternate. A discussion of current policies and ability to serve will
be included.
5
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PLATE 1-1
LOCATION MAP
J-6
SECTION 2
STUDY AREA
The study area will consist of the 506 acres of development area and the water resources
areas of the balance of the 1916 acres of the Arrowhead Springs ownership. There are
areas outside the ownership that may be studied for water supplies and possible discharge
of some wastewater. This will be determined during the study process.
The delineated description of the Study Area is shown on Plate 2-1, Study Area.
The Study Area will include the proposed development areas and the natural areas that
will not include human occupation. The natum! areas could include water resources and
the routing for water conveyance pipelines but; these will be shown on other relative
plates herein.
The man-made and natural landmarks such as highways will be shown so the reader may
orientate himself with the location of areas within the Study Area The sectional surveys
and the periphery of the ownership of the Arrowhead Hotel properties will also be shown
on Plate 2-1.
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SECTION 3
DOMESTIC WATER
3.01 GENERAL
The domestic water system for the Arrowhead Springs development area will be
provided, through either the West Twin Creek Water Company or the Del Rosa
Mutual Water Company, wholly owned companies of the developer, a
combination of both or other entity. The water supply for the domestic water
system will be from wells in the San Bernardino Basin, grOtmdwater on-site and
from stream flows, properly treated to meet State of California. Department of
Health Services, Drinking Water Division, Standards and Requirements. A
network of distribution mains will conduct the water to the places of use and the
construction of reservoirs, booster stations, wells treatment plant and
appurtenances is necessary so the system will provide a high level of service to the
consumers.
3.02 WATER SYSTEM DESIGN CRITERIA
The water system will be designed to provide adequate water service during the
peak hour of the maximwn day or during the maximum day plus fire suppression
flows. The design locations of minimum service will be the most remote and
highest elevation of service in the respective Pressure Zones. To establish this
level of service, the following criteria, is used:
. Average arumal daily water use per person
. Average daily water use per commercial bldg.
. Average daily water use per office bldg.
. Hotels
. Senior facilities
. Average day, maximum day demand
. Maximum day of maximum month demand
. Peak hour of maximwn day
. Minimum hour of maximum day
. Equalization storage
. Emergency Storage
. Fire flow-residential
. Fire flow-commercial
. Minimwn pressure-peak hour
. Maximwn pressure - static
· Occupancy per dwelling unit
J-9
200 gallons
0.4 gpd/sq. ft. floor
0.5 gpd/sq. ft. floor
1.0 gpd/sq. ft. floor
400 gpdlunit
1.50 x average day
2.25 x average daya4.50 x average day
0.50 x average day
0.40 x maximum day
1.00 x average day
Est: 3000 gpm for
2 hour duration
45 psi
125 psi
3.2 people
The hotels are assmncd to have a floor area of 1,250 square feet of gross area per
occupant room. The senior facility is estimated to require 400 gallons per day per
living unit.
All pumping plants will have the sufficient capacity to pump at the design rate of
flow with the highest capacity pump not operating. Design pumping capacity will
have the capacity to pump the maximum day quantity over an I8-hour period or
less. The velocity ofthe water in the distribution mains should not exceed five (5)
feet per second during the peak hour flows. During fire flow periods, the velocity
can be 10 feet per second but, the residual water pressure, away from the fire
hydrant, cannot drop below 20 psi (46 feet of head.).
All water system facilities shall be designed and constructed in accordance with
the applicable standards of the American Water Works Association, The State of
California and the water system operating entity.
3.03 WATER SOURCE
The water supply for the project can come from wells existing on the property,
stream flows in little used watersheds, existing springs and wells constructed off-
site in the San Bernardino Basin. The Arrowhead Springs Project has wells on the
property currently providing domestic water to the facilities and has provided
domestic water during periods of habitation in the past. There are streams within
little used watersheds, which provided water to the hotel in the past and could be
outfitted to deliver future water for domestic use. Prior to use, the stream water
must be treated in accordance with the State Of California "Surface Water Rule",
prior to placing the water in the domestic water system.
A detailed examination of the water sources will be discussed later on in this
doclUTIent to provide the necessary water supply for daily needs and redundancy in
the domestic water system.
3.04 DOMESTIC WATER REQUIREMENTS
The water requirements are a result of population and land use within a given
service area. The historical water use within the service area has been to the
Arrowhead Springs Hotel, outbuildings and support facilities. The hotel has
generally received water from Coldwater Canyon Stream and various wells on the
property. The criteria shown in Section 3.02 above will be applied to the planned
development to create the water requirements. The planned development water
requirements will be converted to "Equivalent Dwelling Units" so a common unit
is created for all water use facilities. An equivalent dwelling unit is equal to the
projected water use of a single-family home. In this respect, the Equivalent
Dwelling Unit is calculated to be 200 gallons per day per person, times an
occupancy of 3.2 people per household or 640 gallons per day, annual average
water use.
The development areas for domestic water, use has been broken down into three basic
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categories: Residential, Commercial and HotelfSpa. Within these categories, a further
breakdown is done to refine the water requirement. Other water uses will be determined
for irrigation, recycled water, water features and water uses, other than domestic uses.
The Equivalent Dwelling Units and Average Annual Daily Water Use are shown in Table
3-1 below:
Table 3-1
Facility Description, EDU's And Average Annual Domestic Water Requirement
Facility Description
EDU's
Water ReQ'd
(Gallons per Day)
RESIDENTIAL
RL-North
RL-South
RM -Residential
RM-Senior
CG-I-VW
TOTALS
76
12
665
188
297
1,238
48,640
7,680
425,600
120,320
190,080
792,320
COMMERCIAL AND OFFICE
RM-Commercial
CG-I-VW
CG-I-WP
CO-1
PCR
TOTALS
8
125
13
195
14
355
5,120
80,000
8,320
124,800
8,960
227,200
HOTEL I CONFERENCE CENTER
CG-i-HlS
CG-I-HlS
CG-l-HlS
250 Rooms + 8 Units
50 Rooms
300 Rooms
TOTALS
504
98
586
1,188
322,560
62,720
375,040
760,320
SUMMARY OF DOMESTIC WATER DEMANDS
Facility Description
EDU
Water Required
Residential
Commercial and Office
Hotel/Spa
TOTALS
1,238
355
1,188
2,781
792,320
227,200
760,320
1,779,840
J-ii
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PLATE 3-1
PROPOSED LAND USE
The average annual daily domestic water requirement is 1,779,840 gallons per day. The
annual water requirement is 694,641,600 gallons or 1,993 acre~feet of water per year.
3.05 PROJECT PHASING
The draft Specific Plan for the Arrowhead Springs Development proposes a two
(2) step Phasing Plan. Project Phasing is generally dictated by the demand for
housing, commercial space and the orderly expansion of utilities. The projected
phasing is shown in Table 3-2, Project Phasing. There is no timetable for the
phasing since development occurs as demands needs are shown.
Table 3-2
Project Phasing
PHASE ONE
Residential
. Rl"-North
. RL-South
. RM-Residential
. RM-Senior
. CG-I-VW
Commercial-Office
. RM-Commercial
. CG-I-VW
. peR
. Public Golf Course
HotelJSpa
. CG-I-H1S-250 Rooms + 8 Units
. CG-I-H/S-50 Rooms
PHASE TWO
Commercial-Office
. CO-l
. CG-I-WP
HoteVSpa
. CG-I-H1S-300 Rooms
Project phasing is shown on Plate 3-2 herein.
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3.06 DOMESTIC WATER PRESSURE ZONES
The domestic water distribution system will require multiple water pressure zones
to accommodate the changing topography in the service area where domestic
water will be provided. Pressure Zones will receive a supply of water to meet the
maximum day of the maximum month requirement for that pressure zone plus the
pressure zones that are higher. Pressure zones will operate from a distribution
reservoir that will hold water for peak hour flows, emergency flows and fire
suppression flows. After the peak demands are met from the reservoir, the water
will be replaced at the rate of flow of the maximum day.
There is an elevation change of over 1,520 feet, requiring 8 separate pressure
zones. The zones will be designed with pressures from 45 psi to 125 psi in each
zone. There will be multiple reservoirs and pressure-regulating stations, which
provide water for domestic use, localized irrigation, fire suppression and
emergency conditions. There will be booster stations, which will raise the water
from the lower reservoirs to the upper reservoirs serving the higher zones.
A Hydraulic Schematic is provided in Plate 3-3, showing the elevations of the
zones, the bottom and tops of the proposed reservoirs, booster station locations
and capacities and capacities for the reservoirs.
Table 3-3 shows the Pressure Zone, Equivalent Dwelling Units (EDU's) estimated
within that pressure zone and the Average Daily Water Requirement for that
particular Pressure Zone.
Table 3-3
Pressure Zones and Water Requirement
Pressure Zone
EDU's
Average Annual Daily
Water Requirement- GPD
49,280
70,400
246,400
1,237,120
128,000
22,400
6,400
19,840
1,779,840
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HI
IV
V
VI
VII
vm
77
110
385
1,933
200
35
10
----TI
2,781
The pressure zone components of land use were developed as follows:
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2370
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SCHEMATIC HYDRAULIC
ARROWHEAD SPRINGS WATER SYSTEM
LEGEND:
i Proposed R~rvoir
i Proposed Booster Station
I Proposed Pressure
Regulator Station
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Table 3-4
Pressure Zone Components and EDU Distribution
Pressure Zone Component EDU Total EDU
I RL-South 2
I RM 75 77
II RL-South 10
II RM 100 110
ill CG-l- VW -Residential 247
ill CG-l- VW -Commercial 125
III CG-1-WP 13 385
IV RM 105
IV RM-Residential 185
IV RM-Commercial 8
IV RM -Senior 188
IV CG-l- VW -Residential 50
IV CG-I-H/S-250 Rooms 504
IV CG-I-H/S-50 Rooms 98
IV CG-1-H1S-300 Rooms 586
IV CO-l 195
IV PCR 14 1,933
V RM 100
V RM- Residential 100 200
VI RL- North 35 35
VII RL- North 10 10
VIII RL- North 31 ~
TOTAL 2,781
3.07 WATER SOURCE REQUIREMENTS
The water system within the Study Area will receive water from the water sources
to the distribution system. The distribution system is within mountainous terrain
and the differences in elevation, requires eight (8) separate zones to maintain
adequate working pressures. Pressure Zone No. IV has the largest water
requirement and the others are smaller. To reduce the number of storage
reservoirs, two (2) zones will be combined, the upper zone will operate directly
from the reservoir and the lower zone will operate through pressure regulating
valves. Water supplies to the pressure zones will be from pumps, suppLying water
J-ILj
sufficient to replace the water during the maximum day of the maximum month
during an IS-hour period. The water supply will be from surface flows treated at
an on-site facility, existing and proposed wells.
Table 3-5 illustrates the water requirement for the proposed development, by a
combination of pressure zones.
Table 3-5
Total Development Area Water Source Requirements
The water source requirements for each combination of Pressure Zones will be
equal to the quantity to re-fill the reservoir from usage on the maximum day of tb.e
maximum month during an eighteen (18) hour pumping period.
Pressure Zones No. I and No. II Combined
Pressure Zone A verage Daily Demand
(gallons per day)
I 49,280
II 70,400
m 246,400
IV 1,237,120
V 128,000
VI 22,400
VII 6,400
VII1 19,840
TOTALS 1,779,840
Maximum Day Demand
(gallons per day)
110,880
158,400
554,400
2,783,520
288,000
50,400
14,400
44,640
4,004,640
Rate-of -flow required over an I8-hour period: 4,004,640/ (18x60) = 3,708
USE 3,800 gallons per minute.
Pressure Zones No. III and No. IV Combined
Pressure Zone Average Daily Demand
(gallons per day)
III 246,400
IV 1,237,120
V 128,000
VI 22,400
VII 6,400
VIII 19,840
TOTALS 1,660,160
Maximum Day Demand
(gallons per day)
554,400
2,783,520
288,000
50,400
14,400
44,640
3,735,360
Rate-of-flow required over an I8-hour period: 3,735,360 I (18x60) = 3,459,
USE 3,500 gallons per minute.
18
J-18
Pressure Zones No. V and No. VI Combined
Pressure Zone A verage Daily Demand
(gallons per day)
V 128,000
VI 22,400
VII 6,400
vm 19.840
TOTALS 176,640
Maximum Day Demand
(gallons per day)
288,000
50,400
14,400
44,640
397,440
Rate-of~f1ow required over an I8-hour period: 397,440/ (18x60) = 368
USE 500 gallons per minute.
Pressure Zones No. VII and No. VIII Combined
Pressure Zone Average Daily Demand
(gallons per day)
VII 6,400
VIll 19,840
TOTALS 26,240
Maximum Day Demand
(gallons per day)
14,400
44,640
59,040
Rate-of-flow required over an 18-hour period: 59,040 I (18x60) = 55,
USE 200 gallons per minute.
Water Sources
The rate of flow for the development at completion is estimated to be three
thousand eight hundred (3,800) gallons per minute. 1bere are several water supply
sources available to the Arrowhead Springs Development. The available supplies
are as follows:
Source
Estimated Supply
TOTAL
500,000 gallons per day
1,000,000 gallons per day
71,000 gallons per day
b533.000 gallons per day
4,104,OOOgallons per day
Coldwater Creek
Strawberry Creek
On-site Wells
Off-S ite- Wells
The off-site-wells would be constructed in the San Bernardino Basin southerly of
the development. The perennial flow in these streams has flowed into the San
Bernardino Basin for a nwnber of years_ The San Bernardino Basin was
adjudicated in the Orange County lawsuit but the Arrowhead Springs area was
outside of the limits of the Basin. Since both the West Twin Creek (Waterman
Canyon Creek) and East Twin Creek (Coldwater Creek and Strawberry Creeks)
are pre 1914 water rights, Arrowhead Springs would discharge water flow from
East Twin and West Twin Creeks to the San Bernardino Basin for withdrawal
1~19
during that water year.
3.08 RESERVOIR SIZING
Each two combined pressure zones will operate from a distribution reservoir with
the upper pressure zone operating directly from the reservoir and the lower zone
operating through pressure regulators. The distribution reservoirs will operate by
gravity flow and the pressure regulators will operate hydraulically, not requiring
outside energy for controls. Each reservoir system will maintain water for daily
operations, emergency water and fire suppression purposes. Each pair of pressure
zones will operate independently from each other except in the case of water
transfers. Water will be transferred during an IS-hour period, with no pumping
from 12:00 noon to 6:00 p.m., the peak hour electrical usage period. This will
save energy and with the power companies giving substantial reductions in energy
rates for this non-use period. This is known as "Time-of-Use" electrical rates.
Since the type of construction is not known, fire suppression quantities are not
known but, we will estimate a flow rate of 3,000 gallons per minute over a two
hour period or a quantity of 360,000 gallons of water in each tank
Pressure Zones I and II Combined
The combined Average Annual Day combined flows will be:
Pressure Zone No. L...........49 ,280 gallons per day
Pressure Zone No. 11.......... 70AOO
TOTAL 119,680 gallons per day
Average Annual Day
Maximum Day-Maximum Month
Peak Hour-Maximum Day
119,680 gpd
269,280 gpd
538,560 gpd
Reservoir Sizing
Fire Flow-3,000 gpm, 2-hour duration
Emergency
Equalization
TOTAL
Use 0.75 million-gallon reservoir
360,000 gallons
119,680
107,712
587,392 gallons
Pressure Zones III and W Combined
The combined Average Annual Day combined flows will be:
Pressure Zone No. m............... ..246,400 gallons per day
Pressure Zone No. IV...............l,237,120
TOT AL 1,483,520 gallons per day
J-16
Average Annual Day
Maximum Day~Maximum Month
Peak. hour-Maximum Day
Reservoir Sizing
Fire Flow- 3000 gpm, 2 hour duration
Emergency
Equalization
TOTAL
Use 3.2 million gallon reservoir
Pressure Zones V and VI Combined
1,483,520 gpd
3,337,920 gpd
6,675,840 gpd
360,000 gallons
1,483,520
1.335,168
3,178,688 gallons
The combined Average Annual Day combined flows will be:
Pressure Zone No. V...... H................ 128,000 gallons per day
Pressure Zone No. VL.............. .......... 22,400
TOTAL 150,400 gallons per day
Average Annual Day
Maxirnwn Day-Maximum Month
Peak Hour-Maximwn Day
Reservoir Sizing
Fire Flow-3,OOO gpm, 2 hour duration
Emergency
Equalization
TOTAL
Use 0.75 million-gallon reservoir
Pressure Zones VII and VIII Combined
150,400 gpd
338,400 gpd
676,800 gpd
360,000 gallons
150,400
135,360
645,760 gallons
The combined Average Annual Day combined flows will be:
Pressure Zone No. VII..................... 6,400 gallons per day
Pressure Zone No. VIII.................... 19,840
TOTAL 26,240 gallons per day
Average Annual Day
Maximum Day-Maximum Month
Peak. Hour-Maximum Day
Reservoir Sizing
Fire Flow-3,OOO gpm, 2 hour duration
J-2~
26,240 gpd
59,040 gpd
118,080 gpd
360,000 gallons
TOTAL
26,240
23.616
409,856 gallons
Emergency
Equalization
Use 0.50 million-gallon reservoir.
3.09 WATER TREATMENT
Water derived from stream flow and possibly some springs will require filtration and
disinfection. Water from wells will require as a minimum, disinfection. Chlorine will be
used as a disinfectant and most likely applied as calcium hypochlorite so no special
construction will be necessary to house and operate chlorine cylinders. Where surface
water is u~ it must follow the State of California Health Department, Drinking Water
Section requirements. This will require several steps to be taken to determine the exact
treatment type. The following is a list of items necessary to obtain approval of the
Coldwater Creek waters for domestic use:
. Perform a "Watershed Sanitary Survey" to the State Standards over
a 12-month period to understand the deviations in water quality
due to climatological conditions.
. Design a water filtration and disinfection system that will allow the
fInished water to meet the requirements of State Drinking Water
Requirements.
. Obtain necessary permits, including a National Pollutant Discharge
Elimination System permit for the backwash and drain water that
will be discharged into dry streams that are tributary to the Santa
Ana River and Pacific Ocean.
To understand the proposed water diversion and proposed treatment process, a schematic
flow diagram is included as Plate 3-5 for Coldwater Creek and 3-6 for Strawberry Creek
3.10 WATER DISTRIBUTION
Domestic water distribution is accomplished through a series of reservoirs, booster
stations, pressure regulator stations and a network of undergrOlUld piping. Water will be
received into the distribution system from the various sources as discussed in Section
3.07 above. The point of receiving the water will depend on the source and may be seen
on Plate 3-3, Hydraulic Schematic. Water will be transferred between reservoirs by
booster stations located adjacent to reservoirs. One reservoir will serve two separate
pressure zone and at the break between these zones, a pressure regulator (s) stations will
be located to provide that zone with water at a pressure between 45 psi and 125 psi. The
water distribution piping network will be designed through a hydraulic network analysis
for the piping sizes to meet the peak hour demands and required fire suppression flows.
During peak hours of electrical consumption, 12:00 noon to 6:00 PM, the distribution
flows will come from the reservoirs to reduce electrical energy costs through "Time-of
Use" pumping. The reservoirs are sized tu contain adequate water for the peak hour
without encroaching upon the fire suppression water and emergency water capacity.
iw~2
During the 18-hour period from 6:00 pm to 12:00 noon, or less, the water source and
boosters will fill the reservoirs to capacity to prepare for the ensuing day_
The transfer of water and monitoring for vandalism will be monitored through an
electronic radio transmission computer controlled system (SCADA system) with
receivers and transmitters at all reservoirs, booster stations and water supply sources to
detect any failures, tampering or unusual condition such as intermittent flows when they
should be constant. Also, if anyone attempts to break: into a facility such as a reservoir,
well, booster pump or treatment plant, the computer will notifY the personnel as
programmed for immediate response.
Disinfection of the water will be done at the location of the water source, such as a well
or treatment plant by a calcium hypochlorite injection system. The system will be
controlled by a meter on the water discharge, telling the system to provide a preset
solution in a quantity comparable to the rate of flow. The chlorinator wiil dissolve tablets
of calcium hypochlorite in to an aqueous solution for injection into the water.
Chlorinators are self sufficient except for the addition of tablets and normal maintenance.
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Feed 1
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Arrowhead Springs
Preliminary Surface Water Treatment System for
Strawberry Creek
Consulting Services
July 2004
J-26
SECTION 4
WASTEWATER
4.01 GENERAL
The present structures within the Study Area are being provided Wastewater collection,
conveyance, trea1ment and disposal by facilities on-site. The treatment is through an
Imhoff Tank style treatment plant that provides primary treatment and the effluent is
discharged into adjacent ponds for evaporation/percolation. The discharge from this plant
is under Board Order No. 86-100, issued by the Santa Ana Regional Water Quality
Control Board. The Board Order will allow a discharge of up to 300,000 gallons per day.
This plant has served the hotel and support structures for many years, but the capacity of
the tank and type of effiuent provided will not comply with the size and style of
development proposed.
It is planned to convey the raw wastewater to a treatment facility in the southerly part of
the project area where the influent will operate by gravity and not require electrical
energy to lift it to the plant. It may be necessary to install wastewater lift stations due to
the mountainous terrain the project is situated. The plant is proposed to provide an
effluent capable meeting the requirements for unrestricted use.
The ne~t existing wastewater facilities are southerly and below the proposed
development, belonging to the City of San Bernardino. The sewers are of minimum
diameter and do not have adequate capacity to provide service to the development. A
second alternate to a wastewater system would be on-sire disposaL The current policy of
the Santa Ana Regional Water Quality Control Board is to allow properties with septic
tanks and underground disposal systems to be constructed at a density of no more than
two single-family homes per acre. The development of Arrowhead Springs will require
significant higher densities; therefore, the use of on-site disposal is not practical.
The study area will be within the service area of the revised service area of the Del Rosa
Mutual Water Company and the West Twin Creek Water Company, which is the total
property of the Arrowhead Development
4.02 W ASTEW A TER QUANTITIES
The amount of wastewater to be generated from the development is a function of the
number of people and the amount of wastewater discharged by each person, the amount
of conunercial area to be constructed. The criteria used to develop the quantity of
wastewater, follows.
J-27
DESIGN CRITERIA
(Daily Contributions)
Contribution per person
Occupancy per dwelling unit
Equivalent Dwelling Unit (EDU)
100 gallons
3.2 people
640 gallons per day
The summation of the above criteria will result in an average daily discharge over on an
annual basis. During the day, the flows will vary with higher and lesser flows than the
average daily flow. The higher flows are computed as "Peak Flows" and calculated by a
factor that is dependent on the average daily flow at that point in the collection system.
The least flow is calculated as fifty (50) percent of the average daily flow. The peak flow
is calculated, based on the following table:
PEAKING FACTORS
Average Daily Flow
(MGD)
Peaking Factor
0.00-0.0 I
0.05
0.10
0.20
0.30
0.50
0.80
1.00
1.50
4.0
3.4
3.2
3.0
2.8
2.7
2.6
2.5
2.4
As may be seen above, the larger the flow, the lesser the peaking factor will be.
The single-family unit, or residence, with an occupancy of 3.2 people, will contribute 320
gallons of wastewater per day.
To place all land uses within the Arrowhead Springs Development on an equal design
basis, the domestic water requirements have been converted to "Equivalent Dwelling
Units" in Table 3-1, Section 3 herein. With wastewater quantities closely following the
domestic water requirements, the Equivalent Dwelling Units developed for domestic
water, they will be used for determining wastewater quantities. A summary of the
"Equivalent Dwelling Units" as shown on Table 3-1 herein is shown below:
SUMMARY OF EQUIVALENT DWELLING UNITS
Residential 1,238
Conune~i~ 355
Hotel/Conference Center 1,188
TOTAL 2,781
}!2s
The quantity of wastewater to be generated by the study area is estimated as follows:
2,781 EDU x 320 gallons per day per EDU, average
daily flow = 889,920 gpd or 0.90 million gallons
per day.
4.03 WASTEWATER COLLECTION SYSTEM
A wastewater collection system will consist of a network of interceptor, collector~ lateral
and service connection sewers all designed and constructed in accordance with the
Sanitary Design and Construction Standards of the Arrowhead Springs Development
serving agency. In general, most of the areas will conduct wastewater in sewers by gravity
flow. Most likely, there will be areas in the mountainous terrain where a wastewater lift
station will be required. This lift station will collect the gravity flow in a receiving
chamber and pumps will lift the wastewater to the elevation where it can flow by gravity
to the wastewater treatment plant.
A general layout of the collection system and wastewater treatment plant is shown on
Plate 4-1.
Sewers will be constructed within paved roads where available and only within easements
when necessary for structure service. All sewers and manholes shall be available for
immediate access by maintenance people and equipment. This is necessary for routine
maintenance and emergency conditions. All federal, state and local safety conditions
including OSHA shall be designed into the wastewater system and all safety orders
followed.
The wastewater collection system will be constructed in phases as development
progresses within the phasing of the project. The collection system will commence in the
lower part of the development where the wastewater treatment plant will be located.
Please refer to Plate 4-1 for the schematic collection system and treatment plant location.
4.04 WASTEWATER TREATMENT
The ultimate wastewater flows have been estimated at 0.9 million gallons per day,
average daily flow (MGD, ADF) when the project is fully constructed and occupied.
Within this Section, the following items will be discussed:
· Develop design parameters for wastewater loadings for wastewater treatment
plant (WWTP) design;
· Describe spray irrigation effluent requirements;
· Describe WWTP treatment process and required redundancy in the design;
· Describe WWTP phasing according to the absorption schedule from development
phasing;
· Describe the spray irrigation process of effluent reuse and provide effluent
parameter limitations;
):29
. Calculate the area required for spray irrigation reuse and describe the necessary
spray irrigation reuse infrastructure;
· Recommend a wet weather wastewater influent storage volwne;
· Describe other design considerations such as noise abatement, odor control, power
requirements and lighting.
The concept for treatment and effluent disposal is to treat the wastewater sufficiently to
obtain an effluent, which 'Will meet Title 22, California Code of Regulations.
WASTEWATER LOADINGS
In addition to wastewater flows, wastewater influent loading is necessary for the design of
the wastewater treatment plant. The standards for calculating biochemical oxygen
demands (BOD) and total suspended solids (fSS) for residential development are listed
below in Table 4-1:
Table 4-1
Design Criteria For Wastewater Influent Loading
Residential Developments
Parameter
Influent Design Value
Biological Oxygen Demand (BOD)
12 Ibs/day/1 000 ft3 of Unit
Volume (300 mg/l)
Total Suspended Solids
12 lbs/d ayl 1 000 ft3 of Unit
V olwne (300 mg/I)
In addition to the residential development, a planned hotel, commercial and recreational
areas are planned and the units design values have been increased to reflect this
development.
EFFLUENT REQUIREMENTS FOR SPRAY IRRlGA TION
Effiuent requirements for treated wastewater are under the jurisdiction of several state
and local agencies. Federal and California state law for reuse water are outlined in the
California Water Code. The State of California Department of Health Services (DOHS)
has mandated reuse water quality standards under Section 13521 of the Porter-Cologne
Act. DOHS has developed comprehensive reuse regulations that establish treatment
processes, water quality criteria and treatment reliability requirements to ensure public
health and safety. These regulations are listed in the California Code of Regulations
(DDR) Title 22. The Santa Ana Regional Water Quality Control Board (SARWQCB) is
responsible for enforcing these regulations to the wastewater producers and users.
Eflluent will be reused by spray irrigation methods on common areas of the development
including parks, golf course, open areas and aesthetic plantings. This type of effluent is
described as Landscape Irrigation in Title 22, Article 4. Since the effluent will be reused
30
J-30
in close proximity of human contact and habitation, a tertiary effluent will be used for
spray irrigation.
Tertiary treated wastewater shall be at all times adequately disinfected, oxidized,
coagulated, clarified and filtered. Effluent limitations are listed in Table 4-2 below:
31
J-31
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Effluent Limitations For Spray Irrigation
Landscape Irrigation
Parameter
Effluent Design Value
Median Number of Coliform Organisms
2.2 per 100 milliliters as determined
from the bacteriological results of the
7 days for which the analysis have
been completed.
Number of Coliform Organisms
23 per 100 milliliters in any sample
Biological Oxygen Demand (BOD)
5mgll
Total Suspended Solids (TSS)
5 mg/l
Turbidity
2 NTIJ
Nitrogen
10 mg/l (current) 5 mgll (future)
Chlorine Residual
5mgll
The proposed WWTP will be designed to meet these limitations.
W ASTEW A TER TREATMENT PROCESS AND REDUNDANCY
a. General
The treatment process being considered for this project is a Micro filtrate membrane
bioreactor, or commonly called micro filtration. This process was considered because of
the compact nature of the plant and reasonably simple maintenance and operation to
provide the quality of effluent for unrestricted irrigation. Typically, the entire process can
be housed within a structure whose architecture will fit into the neighborhood and contain
sound and odor control. The process units can be constructed in phases to accommodate
the progress of development and construction.
b. Treatment Process
An influent lift station will place wastewater at an elevation to enter the Hcadworks
which will contain influent fine screens with a minimum 3/8" opening and an aerated grit
chamber prior to entering thc nitrification/de-nitrification chamber.
A SymBio™ Basin will be provided to receive the screened influent and perform
simultaneous nitrification/de-nitrification using nicotinamide adenine dinucleotide
(NADH) concentration level monitoring. The basin will have a fine bubble aeration
r
J-j3
system with a dedicated blower equipped with a variable frequency drive (VFD). The
operating dissolved oxygen (DO) will be in the range of 0.2-0.6 ppm. There will be a
mechanical mixer to avoid settling at low flowlloading conditions. The treated water from
the basin will be fed to the membrane bioreactor (MBR).
The MBR will be designed to operate at high MLSS (15,000-20,000 mgll TSS) and with
design flux rates at 15 gallons per square foot per day with peaks of 30 gallons per square
foot per day for periods of 6-12 hours. Mixed liquor will be pumped using re-circulation
pumps to the SymBio™ Basin at a rate of2Q.
The membrane cassettes will incorporate integrated diffused air systems.
The MBR wiU contain stacked membrane cassettes with flat panel membrane cartridges
with an average porosity of 0.4 microns. The bottom diffuser case will support the
membrane case and house a coarse-bubble aeration system.
Bubbles generated by the blower are emitted at the diffuser and channeled upward
between each of the membrane cartridges as they rise to the surface. The channeled
bubbles accomplish three important objectives by providing adequate oxygen to maintain
design :MLSS (cell respiration), scouring the membranes to prevent fouling, and creating
a pressure gradient between the top and bottom of the membrane unit.
The pressure gradient created by the rising bubbles induces an upward cross-flow of
mixed liquor over the membranes (0.5 mfs). The liquor is filtered as it flows across the
membrane due to trans-membrane pressure gradient created by liquid head above the
permeate header or by pump.
The flux, or filter rate per area., is directly proportional to the trans-membrane pressure
difference which is roughly equal to the liquid head above the permeate header for gravity
applications. In most cases, approximately two (2) feet of head is required to meet the
design flow conditions and an additional head is required to accommodate the design
peak. flow rate. Since equalization will take place within the nitrification/de-nitrification
basin and the MBR the flux rates will be controlled using flow control valves.
Over time the side water depth to overcome flow resistance due to membrane fouling
increases. At a given depth, the unit (or individual cassettes) must be taken offline and the
membranes flushed. Once cleaned, the water depth returns to its original leveL
On average, it is necessary to chemically treat a membrane unit every six months. The
membrane units are cleaned in-place by injecting, or pouring, a dilute solution of bleach
or oxalic acid into the permeate line. The cassettes are cleaned in-place and should take
about two hours to complete. The chemical used to clean the membrane depends on the
substrate treated in the MBR. For organic substrates bleach is used and for inorganic
substrates, oxalic acid.
Etlluent will flow to the tertiary filters and disinfection units and after disinfection, the
effluent will accumulate in an effluent basin where it will be pumped to a place of use.
34
J-34
The treatment plant will have rednndancy where if any unit fails, there is a standby unit
that will automatically come online. There will be standby generator (s) ready to provide
electrical energy if the normal power source fails. An operator will automatiCaIIYi?
notified if any unit (s) fail or the effiuent or process requires attention. During (I/;
weather, there may be a time where the effluent must be stored rather than used or
irrigation. A thirty (30) day storage facility is required. In this case, a storage facility to
hold 33,000,000 million gallons, or 101.26 acre-feet of effluent must be provided.
Normally this is done in an open pond nearby the treatment plant so the effluent can be
reclaimed and put to irrigation use.
A flow diagram for the treatment process is shown on Plate 4-2.
4.05 WASTEWATER COLLECTION
A wastewater collection system will be constructed to collect sewage from the various
structures throughout the development and conduct the raw sewage in closed conduits
through house connection sewers, lateral sewers, main sewers and interceptor sewers to
the treatment plant. The sewers will be designed with a minimum flow of 2-feet per
second at minimum flow to prevent sedimentation and solids from falling out and a
maximum of 10 feet per second to prevent scouring of the sewers. When constructe<L all
sewers will be tested for tightness with air and manholes tested with water to minimize
leakage into the surronnding soil.
Only when absolutely necessary will wastewater lift stations be allowed to be constructed
and only then when no alternative solution is available. The wastewater will be received
in a chamber and allowed to accumulate until a pre determined level is reached and then
the wastewater will be pumped to a higher elevation, allowing it to flow by gravity. The
mechanical units of the lift station will be located above grolUld and have a secondary
source of energy to pump the sewage if the primary source of energy or the pump on-call
does not operate. The switch over must be instantaneous without delays. At the same
time, a SCADA System will notify an on-duty wastewater operator for inunediate action.
The use of low spots such as an inverted siphon is discouraged. To simply maintain a
shallower depth of the sewer by installing such a device, will not be a reason for its
installation. Close attention to design of the sewers will be necessary to minimize the
possibility of overflows, spills and stoppages that could contaminate the watersheds,
streams and visual aesthetics of the adjacent areas.
4.06 PERMITTING
The planning for the wastewater effluent is to use the water for irrigation. There are areas
of potential use on the property such as:
. Golf Course
. Landscapes
. Roadscapes
· Parks Open Space
J'::~5
. Natural Open Space
. Low combustion fuel areas for perimeter fire protection
There appears to be adequate area that will require regular irrigation, which will utilize
the effluent produced and additional water from the properties. Within Section 5, entitled
Irrigation Water, the water requirements will be examined and quantities detennined.
With the use of the effluent for irrigation, there will be no discharge of the effluent and
therefore, no Report of Waste Discharge will be required from the Santa Ana Regional
Water Quality Control Board. What will be required will be an approval of an
"Engineering Report for the Production, Distribution and Use of Recycled Water". The
approval will be from the State of California, Department of Health Services, Drinking
Water Division, and consulting to the Health Services will be the Santa Ana Regional
Water Quality Control Board, Santa Ana Region and the Recycled Water Unit of the
Technical Branch, State of California, department of Health Services, Drinking Water
Division. The Environmental Impact Report for the project which includes the treatment
plant will be approved with the Specific Plan and the other approvals will come from:
. Site approval for the treatment plant site by the City of San Bernardino
. Engineering Report for the Production, Distribution and use of Recycled Water by
the State Department of Health Services
. Wastewater Treatment Plant Permit from the South Coast Air Quality Control
District
. There will be other permits require for hazardous material handling, stonn water
containment and similar items.
36
J-36
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SECTION 5
IRRIGATION WATER
5.01 GENERAL
Irrigation Water will be provided through four separate sources; (1) recycled water from
the wastewater treatment plant; (2) stream flows on the property; (3) wells from San
Bernardino Basin; and (4) ..Steam Cave Well". The wastewater will be a constant flow,
increasing as the development occurs. In the early stages of development, the waters from
Waterman Creek (West Twin Creek) will be used to supply the irrigation needs. This
water will be diverted from the stream and allowed to settle prior to use. As water from
the wastewater treatment plant becomes available, it will be mixed with the stream flows
and used. During the development period of the Arrowhead Springs Project, the quantity
of effiuent will increase, as the properties are occupied. Supplemental water will be
provided from a redundancy well in the San Bernardino Basin. Water for use in irrigating
the "low combustible fuel areas" surrounding the existing developed area is provided by
'.Steam Cave Well".
5.02 IRRIGATION REQUIREMENTS
Irrigation is proposed to take place on the following areas:
. Golf Course
. Parks
. Selected Open Space
. Landscapes
. Roadscapes
. Low Combustion Fuel Fire Breaks
The golf course is proposed as a championship sized course and the irrigated area is
estimated at 199 acres. Of this area, 100 acres are estimated to be irrigated with the
remaining area in lakes, hardscapes and the like. With this area under irrigation, the initial
quantity is estimated to be 780 acre-feet annually, based upon an 80 acre course in the
general area requiring 625 acre feet. Watcr requirements vary with the weather being the
principal reason causing the growth to increase or decline with precipitation and
temperature. The following table 5-1 shows the annual deviations of water requirements:
38
J-38
Table 5..1
Golf Course
Irrigation Water Demands
Based on
780 Acre-.Feet Annually
Month
Use
Factor
Irrigation
Demand
(Ae. Ft.)
22.6
30.4
49.9
74.1
100.6
106.1
120.1
103.0
74.9
52.3
28.1
17.9
January
February
March
April
May
June
July
August
September
October
November
December
0.029
0.039
0.064
0.095
0.129
0.136
0.154
0.132
0.096
0.067
0.036
0.023
Daily
Requirement
(Million Gallons)
0.238
0.354
0.524
0.805
L058
1.152
1.262
l.083
0.814
0.550
0.305
0.182
The irrigation of areas other than the golf course will be from non-potable water, the
same as the golf course. There will be some integration of the two systems for the sake of
simplicity and redundancy, so that both areas will have the benefit of all waters available.
The actual areas of irrigation have yet to be specifically designed and delineated so that
an accurate area of land can be computed. Areas such as the lawns and ornamental
planting around such facilities as hotels, office buildings, conunercial areas, parks,
common spaces, roadscapes and other public and private areas can be irrigated and the
domestic water saved. We have estimated the landscaped ar~ deducting the golf course
at 250 acres.
To serve this 250 acre irrigation area, we estimate that an annual application of five feet
(5') of irrigation water. lbis results in a quantity of 1,250 acre feet annually.
The area to be maintained as a low combustible fuel area has not been clearly established.
The irrigation of this area will not be a continuous application, but only when natural
moisture is not present for plant growth and maintenance. For this fuel break, we estimate
an area 200 feet in width with a length of 10,000 feet. The golf course in many areas will
act as a fuel break, reducing the designated area. The estimated water application is 2.0
feet annually. 'This will convert to a quantity of 12.3 acre-feet of water annually. Much of
this will depend upon the plant species used and the natural precipitation in the area. The
low combustible fuel area is proposed to be irrigated only with stream water since
domestic water will be taken from Coldwater Canyon and Strawberry Creek. The water
application period is presently proposed to be during the months from June through
November. This six month period would require an even application of about two (2) acre
feet per month except when a fire may threaten the area, then extra water application for a
39
J-39
short period may be called for.
The annual application rate for the 1,250 acre feet of irrigation water will be similar to the
golf course and the following Table 5-2 illustrates the application rate.
Table 5-2
General Irrigation
1,250-Acre Feet Per Year
Month Use Factor Irrigation Daily
Demand Requirement
CAe. Ft.) (MGD)
January 0.029 36.25 0.381
February 0.039 48.75 0.567
March 0.064 80.00 0.841
April 0.095 118.75 1.290
May 0.129 161.25 1.695
June 0.136 170.00 1.847
July 0.154 192.50 2.024
August 0.132 165.00 1.734
September 0.096 120.00 1.304
October 0.067 83.75 0.880
November 0.036 45.00 0,489
December 0.023 28.75 0.302
To understand the total irrigation water requirements and the estimated distribution of
monthly deviations in arumal average estimated requirements, the combined totals are
summarized. The golf course, general irrigation and low combustible fuel areas are
shown in Table 5-3 and summarized so that the necessary ultimate water source is known.
Month
January
February
March
April
May
June
July
August
September
Table 5-3
Summary of Irrigation Demands
(Shown in Million Gallous per Day)
Golf General Fire
Course Irrigation Break
0.238 0.381 -0-
0.354 0.567 -0-
0.524 0.841 -0-
0.805 1.290 -0-
].058 1.695 -0-
1.152 1.847 0.022
1.262 2.024 0.022
1.083 1.734 0.022
0.814 ] .304 0.022
40
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Total
0.619
0.921
1.365
2.095
2.753
3.021
3.308
2.839
2.140
October
November
December
0.550
0.305
0.182
0.880
0.489
0.302
0.022
0.022
-0-
1.452
0.816
0.484
The maximum daily irrigation water requirement is shown for the average day of July for
a quantity of 3308 million gallons. The average quantity will be increased by fifteen
percent (15 %) to account for any increase in anyone day. This results in an estimated
requirement of 3.08 million gallons for the highest daily requirement and this is the
quantity that the water source must be designed for.
During the construction period, particularly during the earthwork period early on, water
will be required for compaction and dust controL Depending upon the amount of earth
moved, the water quantity needed will vary. We can anticipate a need of about 500,000
gallons per day but this can change.
5.03 IRRIGATION WATER SOURCE
There will be two sources of irrigation water, recycled wastewater and stream flow. Upon
completion of the project and occupancy has occurred, we would expect a recycled water
flow of eighty five percent (85%) of the designed flow or 0.765 million gallons per day.
Waterman Canyon Creek (West Twin Creek) will be the surface water source with the
diversion point being at the historic West Twin Creek Water Company diversion.
Domestic water will be diverted from East Twin Creek, Coldwater Creek and Strawberry
Creek. Historically, the hotel received drinking water from coldwater Creek and
irrigation from Strawberry Creek with the Del Rosa Mutual Water Company diversion
point downstream.
Initially, there will be little or no wastewater to be recycled for use. The treatment plant
must be permitted, designed, constructed and tested along with the completion of the "
Engineering Report for the Production, Distribution and Use of RecycIed Water" must be
processed through the State Department of Health Services, Drinking Water Division.
Site approvals and a completed EIR, covering the Treatment Plant must be certified. If the
treatment plant EIR is included with the Specific Plan, the processing of the treatment
plant permitting will take a minimum of 12 months and more like 18 months if all goes
welL
There is a Preliminary Absorption Schedule for the Arrowhead Properties, which is quite
aggressive, showing a build-out within three and one-half years after start of construction.
The first six (6) months of construction will include infrastructure implementation and it
will require the construction of the domestic water system source of supply, distribution
reservoirs, pipelines and fire hydrants prior to the delivery of combustible building
materials to the site. At the same time and possibly lagging some, the construction of the
wastewater treatment plant must be completed. For both the domestic water system and
the wastewater system, the facilities will be constructed in phases to complement the
construction of habitable structures. The Preliminary Absorption Schedule is shown on
Plate 5-1. If we assume a straight line occupancy over the three (3) year construction
period, the generation of recycled wastewater will be as shown below in Table 5-4.
41
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Table 5-4
Preliminary Recycled Wastewater Generation Schedule
Year 1............ ........ .......... ......296,640 gpd
Year 2.. . .. .. . . . . . . .. . . . . . .. . . . . .. . . .. . . . . 593,280 gpd
Year 3......... ...... ..... ............. ...889,920 gpd
The average annual flows within West Twin Creek, (Waterman Canyon Creek) have
averaged 2,491 acre-feet per year. There have been years when the flows have been
higher and much lower. There have been years such as 1961 when West Twin Creek
discharged only 192 acre-feet of water. The deficiency of water must be made up from
other sources such as wells in the San Bernardino Basin. The 2030 acre-feet of irrigation
water required less the 997 acre-feet of recycled water, leaves 1,033 acre-feet to be
produced from stream flow, wells or a combination of both. In normal years, the stream
can provide adequate water but during low flow periods, alternate water sources must be
made available.
The irrigation areas will have ponds and reservoirs for redundancy within the water
source system. There will be a redundancy well within the San Bernardino Basin to
provide water to the domestic water system. Water could be produced from this well and
distributed through the irrigation system to make up any deficiencies
5.04 IRRIGATION WATER DISTRIBUTION
The water produced from the various sources must be accumulated and distributed to the
places of use. The water must be available for "on-demand" use at any time at any
location within the development. There must be redundancy within the system to provide
a continuous source of usable water. The stream flows must have the deleterious material
removed by screening or filtration so the water, may be applied by sprinklers. The well
and recycled water will not require this process. To collect the irrigation water sources so
they may be distributed to the proper places of use, the following description and Plate
No. 5-2 will delineate this plan:
. Collect the water sources from West Twin Creek, East Twin Creek (Del Rosa
Mutual Diversion, Recycled Water from the wastewater treatment plant and any
needed water from the redundancy well in the San Bernardino Basin. This
collection point will be an existing pond proposed for irrigation uses and not used
today for that purpose.
. Allow water to irrigate areas down gradient from this pond.
. A booster station at this pond will lift the water to two reservoirs at the same
elevation, one with a capacity of 1.5 million gallons and the other 0.75 million
gallons. The booster station would have a capacity of 3,100 gallons per minute.
. The areas down gradient from these reservoirs would be furnished water,
including the golf course and its lakes.
. The runoff within the drainages to Coldwater Creek and Strawberry Creek would
be controlled so no runoff would leave the irrigation area and reach those streams.
42
J-42
. At the 0.75 million gallon reservoir, there will be a booster station with a capacity
of 800 gallons per minute to lift the water to another 0.75 million gallon reservoir
at the upper end of the development.
. There is, an existing wann water well known as the "Steam Cave Well" which
can be used to irrigate the "low combustible fuel area" on the nQrtherly and
easterly areas surrounding the existing developed area to inhibit or slow wildfires
from reaching the development.
The pipelines for irrigation will be located in roads and rights of ways in which domestic
water is located. To distinguish one conduit from the other, the State Department of
Health Services, Drinking Water Section calls for pipelines carrying recycled water to be
colored "Purple", Where non-potable water is being carried and does not have any
recycled water, the international color for non-potable water will be used. This non-
potable pipeline color is yellow.
As the development occurs there are most likely changes to the irrigation areas and
requirements that will modifY the facilities and changes will occur. This is a backbone
system that can adapt to those changes and is flexible enough to remain viable.
Within the system, there is one day of storage for gravity flow without the need from the
golf course lakes and other water features within the project. The non-potable water
system for the irrigation of the low combustible fuel area has a reservoir of 0.50 million
gallons capacity that will contain about 22 days of use. This will allow heavier watering if
a fire approaches or if the power is out at the well, there is ample water for use.
43
J-43
PLATE 5-1
ABSORPTION SCHEDULE
44
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