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LAKE CAI.AVERA HILLS RECLAMATION STIIDY
EXECUTIYE SU~Y
The purpose of the study is to answer the following questions:
I. NON-POTABLE DEMANfi
A. Amount of Dem, nd
B. Location of D:mand
C. Pennanance of Demand
II. FACILITIES REQUIRED TO COMPLETE RECLAMATION PROGRAM
A. Sewage Disposal
B. Water Reclamation
III. WHEN SHOULD RECLAMATION PROGRAM BE STARTED?
IV. WHAT ARE THE COSTS FOR THE RECLAMATION PROGRAM?
MARKET
There are many areas within the City of Carlsbad that could have a
demand for non-potable water. However, in order to reduce capital and
operating costs it is necessary to identify those markets that require
the least amount of expense. A recommended service area has been
developed as shown on Figure 1 which includes lands lying north of
Palomar Road east of Interstate 5 and west of El Camino Real. These
areas were selected because they represent a potential demand greater
than the pl ant out.put and they are in an area that does not require
demineralization. Further, the proposed disposal 1ine traverses much of
the area that could be served non-potable water, thus creating further
economies in system distribution and layout.
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LEGEND
EXISTING PIPELINE
PROPOSED EDL
EXTENSION
PROPOSED
DISTRIBUTION LINE o
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PROPOSED
SERVICE AREA
PROPOSED SERVICE
AREA MAP
FIGURE 1
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_.,.-LAKE CALAVERA HILLS
., RECLAMATION PLANT
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AGRICULTURE
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HUNINGTON
PROPOSED
STORAGE
RESERVOIR
········· ········· AIRPORT
CARLSBAD
RESEARCH
CENTER
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In addition, the operating storage reservoir for the reclaimed
water system can be centrally 1 ocated within the s,ervi ce area; an
extension of the potable water system to this reservoir provides supple-
mental water during those t1i11es when the demand exceeds the output from
the reclamation facility.
It has been detennined that the success of a reclamation program
can depend upon the quality of service provided to the customer. Non-
potable water service should be like potable water service, in that the
customer should be able to draw water when it is needed in the
quantities needed; thus, the necessity of having potable water available
to make up any deficiencies.
By serving an area with a demand greater than plant output,
seasonal storage requirements would be reduced; thus, reducing capital
expenditures as well. The reclaimed water should be viewed as another
source for the City's non-potable demand in the overall water management
program.
Table 1 is a summary of the projected demands within the service
area during the period 1983-2003. It can be noted that demand exceeds
plant production.
Year
1983
1988
1993
1998
2003
Table 1
PROJECTED IRRIGATION DEMANDS WITHIN STUDY AREA
(Average Dry Demand -MGD)
Agricultural Landscape
(1) Irrigation Macario Park
0.96 0 0
0.96 0.11 0
0.96 0.22 0.16
0.96 0.32 0.24
0.96 0.43 0.32
Totals
0.96
1.07
1.34
1.52
1.71
1 Assumes minimum of 360 acres are irrigated within 560 acre ag ri-
cultural area (65% of possible demand).
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A large portion of the estimated demand would come from land now in
Agricultural Preserve. Should this land be removed from the Preserve
and develop into an urban use, t~e total demand from the service area
would be ;·educed to an amount approximately equal to the Lake Cal avera
Hills plant flow. This would increase the required size of seasona1
storage. However, an alternative to increased storage would be to
extend service to areas south of Palomar Airport Road. Because of the
time required for lands to be removed from Agricultural Preserve and the
probable long-term phasing of these lands from agricultural use to urban
development, increased storage or extension of service to areas outside
of the proposed service area wou 1 d not be required unt i1 beyond the year
2000.
AVAILABILITY OF RECLAIMED WATER
Development within the Lake Calavera Hills sewer service area is
projected to occur over a 20-year period. Estimated flows in 5-year
increments for Lake Calavera Hills are summarized in Table 2.
Table 2
PROJECTED RECLAMATION WATER PRODUCTION
Year Flow (MGD)
1983 0.20
1988 0.43
1993 0.68
1998 0.94
2003 1.20
Figure 2 provides a graphical summary of projected irrigation
demand and reclaimed water production.
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SERVICE AREA IRRIGATION DEMANDS
& RECLAIMED WATER PRODUCTION
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ESTIMATED
IRRIGATION DEMANDS } -,,,--·-I
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,4: WA TEA PRODUCTION
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1983 1988 1993 1998 2003
TIME FIGURE 2
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RECLAMATION PLMIT FACILITIES
Development of a non-potable water program requires certain modifi-
cations to the existing lake Calavera reclamation facility. These
modifications are required to meet not only market conditions, but
regulatory agency requirements as well.
These facilities are listed in Tables 3 and 4 along with their
estimated costs. lhe etfluent disposal line cost included in Table 3 is
needed to complete the Ldke Calavera Hills treatment system. The facili-
ties itemized in Table 4 are those required tu develop the reclamation
program.
Table 3
ESTIMATED SEWER SYSTEM IMPROVEMENT COSTS
Item Estimated Cost
Effluent Disposal line $ 681,700
Table 4
ESTIMATED RECLAMATION SYSTEM IMPROVEMENT COSTS
Item
Treatment Plant Improvements
Operational Storage (1.2 mg)
Distribution Mains
Water Line Extension
Seasonal Storage {50 mg)
TOTAL
Estimated Cost
$1,753,200
432,500
242,600
80,000
1,500,COO
$ 4,008,300
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Improvements required within the Lake Calavera Hills plant include
the addition of clarification, filtration and extended chlorination
facilities in order to provide treatment levels sufficient to meet State
Heal th Department requirements. These improvements would a 11 ow use of
reclaimed water throughout the service area for agricultural and land-
scape irrigation purposes.
It has been detenni ned that with the potential demand shown in
Table 1, seasonal storage can be reduced to approximately 50 million
gallons.
RECLAMATION PROGRAM TIMING
Determination as to when reclamation should be implemented is
dependent, on a large measure, on the basic assumptions used in the
analysis. In this instance, the study assumes that only those costs
attributable to wastewater reclamation will be used in comparison to
imported water; thus those costs attributable to wastewater disposal ,
such as the Encina treatment facility, have been subtracted from the
cost of producing reclaimed water. The situation is further complicated
by Encina's application for a waiver as this would materially effect
what would be considered disposal cost. Currently, it is anticipated
that, as of July 1, the treatment cost will be $485 per million gallons.
However, if a waiver is granted, this cost could be JS low as $250 per
million gallons; thus, it was necessary to take these two parameters
into account in estimating the proper time to implement a wastewater
reclamation program.
Costs of wastewater reclamation were developed on an annual basis
through the 20-year period. This was necessary because in the initial
start up, with low flows, unit costs will be higher. However, as the
flows increase, plant efficiency will increase, thus decrea~'.ing the unit
cost for water production; however, this will be offset by inflationary
trends. These are depicted in Figures 3 and 4.
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COMPARISON OF WATER SUPPLY COSTS
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/ PROJECTED COST OF ~ /
IMPORTED WATER _,"1'
(AGRICULTURAL RATE) / ~~
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PROJECTED NET COST
OF RECLAIMED WATER
(ASSUMING SECONDARY
TREATMENT AT ENCINA)
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1982 1984 1986 1988 1990 1992 1994 1996 1998 2000 2002
YEAR
FIGURE 3
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COMPARISON OF WATER SUPPLY COSTS
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2
PROJECTED NET COST
OF RECLAIMED WATER
(ASSUMING ADVANCED
PRIMARY TREATMENT
AT ENCINA)
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IMPORTED WATER /
(AGRICULTURAL RATE) ~/
PROJECTED COST OF -j
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1982 1984 1986 1988 1990 1992 1994 1996 1998 2000 2002
YEAR
FIGURE 4
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These costs were then compared to the anticipated costs for
imported agriculturai water. Forecasting future water prices is more
difficult, in that they are not subject to the same inflationary forces
as reclamation. We know that the Metropolitan Water District of
Southern California will be raising its price for water in the next two
years, approximately $30 per acre-foot per year, <iue to adjustment in
power contracts (an increase of approximately 20% per year).
However, Metropolitan Water District has no definite program for
predicting f11ture cost increases. Currently, Metropolitan has a policy
of funding capital debt service between taxes and water rates which will
probably change in the forthcoming years. In fact, there is a!; outside
chance the Agricultural Rebate Program could be reduced, putting further
pressure on increased water prices. Taking all these factors into
account, a conservative projection of a 10% annual increase in water
rates was used as a comparison to reclaimed water production costs.
rhe projected cost of imported water is shown in Figures 3 and 4.
It can be noted that wastewater reclamation costs fall below imported
water costs in approximately 1985, assuming Encina costs are at $485 per
million gallons. Should Encina obtain a waiver, the crossover point
then shifts to approximately 1988-89. These curves do not take into
account capital facilities, only operational costs. It is assumed that
capital costs would be collected through sources other than water sales
income.
SUMMARY
There is a definite market for a non-potable supply of water for
the foreseeable future. The market is in an a"'ea that lends itself to
the efficient distribution of the water. Further, it is in a basin that
does not require demineralization. The proposed system is flexible and
is readily adaptable to meet demand needs where they occur.
There is sufficient time to prepare for the implementation of the
proyram, thus ensuring the economic viability of the project at the most
opportune time. As noted in the exhibits, reclamation should become a
viable economic program in the middle or late !980 1 s.
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