HomeMy WebLinkAbout; Lake Calavera & Mission Basin Well Field; Lake Calavera & Mission Basin Well Field; 1984-04-14A REPORT ON
THE EVALUATION OF LAKE CALAVERA
AND MISSION BASIN WELL FIELD
AS WATER RESOURCES
CITY OF CARLSBAD
APRIL Ht, 198*f
A REPORT ON
THE EVALUATION OF LAKE CALAVERA
AND MISSION BASIN WELL FIELD
AS WATER RESOURCES
I. SCOPE OF STUDY
The scope and purpose of this study is to evaluate Lake Calavera
and the well field located in the "Mission Basin " (basin) as to
their potential for integration into the water system of the City
of Carlsbad or, in the alternative, to recommend other
utilization of these assets.
The study consisted of field inspections, discussions with the
Water Utilities Director of Oceanside, consultation with expert
hydrogeologists and examination of all available reports
relative to the subject areas, including some furnished by the
City of Carlsbad. All major water rights, appropriation,
diversion licenses and permits were investigated.
Special thanks is given to Roger Greer, Director
Utilities/Maintenance of the City of Carlsbad for his time and
assistance, as well as Jim Turner, Water Utilities Director, City
of Oceanside, and Bob Coates, Project Manager.
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II. DESCRIPTION OF FACILITIES
A. LAKE CALAVERA
The City acquired Lake Calavera and a permit to divert 150 acre
feet of water from Calavera Creek from the Carlsbad Mutual Water
Company. The original license was for irrigation purposes, later
changed to recreational and fire protection purposes.
In addition to the water rights of the lake, the City owns some
252 acres of land. The lake is currently used in a marginal
manner for flood control, but no beneficial use of the water is
presently made.
The property is surrounded on the west side by residential
developement and appears to lend itself to such developement.
Utilities are available nearby to serve the property and improved
streets provide access. The topography is gently rolling,
sloping generally toward the lake near its center.
B. WATER RIGHTS
The City owns a series of wells, "sump" pumping station and
transmission facilities for the production and delivery of water
from the "Mission Basin" of the San Luis Rey River Valley in
eastern Oceanside.
The City has rights to 2,382 acre feet of water from the basin
traceable to 1914. In addition, the City holds a license
(terminable by the State Division of Water Rights, Department of
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Water Resources, from year-to-year) for another 1,000 ACFT.
This basin was historically the site of large truck farms and
citrus orchards. Groundwater pumped from the basin was used
extensively for irrigation and for export to the Cities of
Carlsbad and Oceanside. Since the 1950's , pumpage has declined
considerably because of increasing concentrations of dissolved
solids in the groundwater. In 1958, the City of Oceanside began
transporting reclaimed sewage to Whalen Lake on the northwest
side of the valley, but that practice has since been abandoned.
The basin is bounded mostly by marine deposits of Tertiary Age.
The groundwater in the surrounding deposits is saline. The San
Onofre Breccia borders and underlies the basin on the downstream
western edge and is composed of cemented sand, sandy shale and
shale that are of low permeability. The rest of the basin is
underlain by the La Jolla Group which consist of fine grained,
well compacted, and slightly cemented shale. This formation is
only slightly permeable.
Overlaying the marine deposits is a thick layer of younger
alluvium and river channel deposits of clay, silt, sand, and
gravel which attains a maximum thickness of 220 feet. Parts of
this very permeable area are covered by a layer of fine sand,
silt, and clay which confines the groundwater in the underlying
aquifer.
tii^wi^i iti|ii|jiii
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Seawater intrusion, as well as lateral and upward movement of
saline water from older marine deposits, have occurred during
periods of low water levels, contributing to the quality
problems. Inflow of inferior water from upstream in the San Luis
Key River is the primary contributor to inferior quality when
water levels are maintained.
Due to the gradual degradation of water quality and an overdraft
problem in the basin, the City abandoned all attempts to utilize
the water when imported sources became available.
The City of Oceanside holds basin water rights totalling 18,000
ACFT. The combined pumping of the basin resulted in serious
overdraft and increased salt water intrusion. The City of
Oceanside reports a well west of the Carlsbad well field, with a
total dissolved solid level above 17,000 mg/1.
Examination of the wells, pumping equipment, and pipelines making
up the well field system reveals that all of these facilities
would need extensive repair, if not total reconstruction.
Detailed estimates were not made, but it is estimated that a cost
of $500,000 to $750,000 would be required for the wells alone.
There appears to be no justification to rebuild the transmission
system as the water could be "wheeled" through the Oceanside
system.
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III. EVALUATION OF WATER RESOURCE POTENTIAL
A. LAKE CALAVERA
The water production from Lake Calavera appears to be very
limited. Water has been released from time to time during
periods of high precipitation, but apparently not on a regular
basis.
The cost involved in putting the limited quantities of water
available to beneficial use for domestic purposes are obviously
prohibitive. Health Department Regulations require that surface
waters be fully treated prior to introduction into the potable
water system. The cost to construct facilities to treat the
small amount of infrequently occurring water would be much
greater than the comparable cost of imported water.
A possible use of the impounded surface water, mixed with
reclaimed water, might be for irrigation purposes, but
examination of that potential proved fruitless as well. The cost
of pumping and transmission facilities to deliver the water to
the nearest point of use would not be justified for the
quantities available.
Without the expense of detailed cost estimates and cost benefit
analysis, the conclusion may be drawn that Lake Calavera has no
potential as a water resource. The Lake and surrounding property
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have value to the City far exceeding any water resource value as
discussed under RECOMMENDATIONS below.
B. BASIN CONDITIONS
The water levels in the Mission Basin have recovered considerably
in past years with the reduction (near cessation) of pumping.
Quality, however, remains unacceptable for any use. There has
been no material change from prior sampling history, based upon
recent test results obtained from the City of Oceanside. Maps
are attached as exhibits, graphically depicting the water
quality.
In essence, the quality of water in the basin is not useable
without demineralization. The value of the storage potential and
the future value of the water when treatment becomes economical,
would indicate that the City should preserve it's rights to the
water and continue to explore the various alternatives listed in
RECOMMENDATIONS below.
IV. RECOMMENDATIONS
A. LAKE CALAVERA
As discussed above, there appears to be no "cost-beneficial" use
of the limited water resources represented by Lake Calavera.
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It is recommended that the property be declared surplus and a new
appraisal be commissioned preparatory to sale. The last
available appraisal was done in 1974 by Robert M. Dodd &
Associates and concluded a market value of $1,900,000. In as
much as the lands available for residential development proximate
to the City proper have been greatly reduced since that time and
values have increased dramatically, a new appraisal is in order.
Sale of the property surrounding the lake with retention of the
"flooded " area for it's limited flood control value (and
residential development enhancement) would appear to be in the
best interest of the City. San Diego County and possibly other
government agencies may have a "right of first refusal" but the
City could receive market value for the property.
Obviously, the City Council would be free to utilize the sale
proceeds as it sees fit, but if the decision was made to retain
the funds in the Utilities Department, there would probably be
enough to carry out the recommendation regarding the basin and
we 11 field.
B. WELL FIELD AND BASIN RIGHTS
As noted in the above, the existing groundwater quality is
unsuitable for potable or even non-potable usage with a TDS of
1800 mg/1.
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One alternative would be for the demineralization of the water as
it is pumped from the ground. In the past, it has been generally
concurred that demineralization was not an economic alternative
as the cost of imported water was much lower than the cost of
demineralization. However, the recent price increases for
imported water in relationship to the demineralization process,
requires another examination of this possibility.
In addition to the rising imported water costs, technology has
now improved to permit the use of lower pressure membranes for
the Reverse Osmosis (RO) process. The current membranes require
pressures of approximately 400 to 450 Ibs/sq. inch. Research
performed by Water Factory 21 in Orange County now indicates the
feasibility of using a low pressure membrane at approximately 250
PSI. Recent technology indicates there is an opportunity for this
to go down to 150 PSI - probably in the next 5 years.
Capital Costs
Appendix 1. is a summary of the capital costs associated with the
development of an RO facility to demineralize basin waters to a
blend of approximately 500 mg/1, producing 2300 ACPT on an annual
basis.
Operating Costs
The operating costs for such a facility have been based upon
actual data prepared by Water Factory 21. (Appendix 2.) The
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results of this analysis have been plotted (Appendix 3.) in
comparison with imported water.
Several inflation rates were used in an effort to develop a
'window of opportunity1 or at least measure the sensitivity of
demineralization versus imported water. For comparison purposes,
a value of $50/ACFT was given to the groundwater as the market
value of emergency storage. This $50 was deducted from the
production costs for demineralized water.
Demineralized vs. Imported Water
You will note that the feasibility of using demineralized water
occurs between 1988 and 1995, depending upon the degree of
inflation experienced by either the imported water or the
demineralization process.
It appears the cost of imported water will experience rather
dramatic increases in the next year or two to account for
Metropolitan's contract with the State Water Project, as well as
the development of the Delta Transfer facility. Taking this into
account, Appendix 3 depicts the impact upon imported water versus
demineralization should the State assess Metropolitan for these
new facilities. This indicates that demineralized local water
becomes quite feasible.
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Transfer of Water
The analysis also indicates there can be a minimal expenditure of
capital funds if the City of Carlsbad can transport their
demineralized water to the City of Oceanside and work out a
•wheeling' arrangement where water drawn from the well basin can
be traded in like quantity in some other part of the Carlsbad
system. Thus, eliminating the need of re-constructing any major
pipelines for the distribution of water from the well field back
to the City's distribution system.
Joint Use
In addition, it may be desirable to participate in a 'joint'
demineralization facility (Carlsbad/Oceanside), as the economies
of scale could represent further savings in the development of
this natural resource.
Advantages
The development of local water resources provides 3 advantages.
(1) It is an emergency source of water in case of an aqueduct
shutdown, (2) it takes advantage of local resources at a
potential savings to the ultimate consumer, and (3) it provides
storage that is not subject to evaporation problems or surface
polution.
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Financial Considerations
The foregoing analysis indicates that the demineralization of
cbasin waters will, in all probability, become economically
feasible within the next 5 to 10 years. This financial
feasibility could be further enhanced by participation in
Metropolitan Water District's Local Projects program. With
greater emphasis being placed upon the development of local
resources, much of Metropolitan's focus will be directed to such
areas. The technological breakthrough with low pressure
membranes provides encouragement for this program.
RECOMMENDATIONS
Groundwater Enhancement
The City of Carlsbad should consider a Joint Development program
with the City of Oceanside for the use of the basin waters and
the enhancement of a Water Quality program in the tributary area.
As Oceanside owns rights to 18,000 ACFT, it obviously has a
greater interest and need but would seem to welcome cooperation
with Carlsbad.
The scope of this study is limited and cannot provide sufficient
detail or any firm recommendations regarding the exact method of
treatment nor the affiliated costs for a specific method.
itmiKlj. 'IB**!*'JB
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Should the City decide to proceed with this project, it is
recommended that a careful examination be made of all the
demineralization techniques available at this time, such as;
electro-dialysis, as well as Reverse Osmosis.
There may also be an opportunity to relocate the wells to areas
of better water quality, further decreasing the operating cost
for the demineralization process and making it possible to sell
the more expensive lands located near Mission Avenue.
One further recommendation is that the City consider undertaking,
jointly with Oceanside, a study of the possibility of a
subsurface dam in the Bonsall Narrows area which would stop the
migration of poor quality subterranean which is continuing to
degrade the basin quality. If the inflow to the basin is surface
flow, primarily storm flow, at the same time the poor quality
water is being demineralized and removed, there should be a
gradual improvement in the water quality. More study and some
testing would be required to thoroughly evaluate this approach,
but the potential benefits would appear to justify it.
A DD ND
Glenn U. Reiter &
APPENDIX 1.
CAPITAL COSTS FOR 1.4 MGD RO PLANT & FACILITIES
Item Description
1.4 MGD Reverse Osmosis plant
3 New Wells
I Pump Station
1500 GPM (3001) (160HP)
1000' of 12" Pipeline
TOTAL
Cost
$1,000,000
300,000
160,000
30,000
$1,490,000
Assume 20 Year Loan at 10%$175,000 per Year
A DD
Ciann U—R*it«r * A««ooiota«
APPENDIX 2.
OPERATING COSTS FOR 1.4 MGD RO PLANT & FACILITIES
Energy requirement to demineralize l MG of water - low pressure
membrane operating at £50 PSI = 3,500 KWHR.
Electrical Energy Cost
Chemicals
Membrane Replacement
0 & M
Sub-total (Note 1)
Well Energy
2,300 x 26 =
1,840 ACFT x 308 = (Note 2)
Total
Divide by 2,300 ACFT =
Add Capital Cost
Sub-total
Less Underground Storage Credit
Net Cost of Water
3,500 x $0.13
or
S455/MG
$148/ACFT
$38
$89
$33
$308/ACFT
$26/ACFT
$59,800
$566,720
$626,520
$272/ACFT
$76/ACFT
$348/ACFT
$50/ACFT
$298/ACFT
Note: 1.) Assume Product Water Q 175 mg/1.
2.) Treat 1,840 ACFT and blend to get
2,300 ACFT @ 500 mg/1.
A DD
Glann M. Reitar A
! II il II II ii ii ii ii ii ii ii ii ii 11 ti 11 ii ii ii
WATER COST COMPARISON
IMPORTED v.s. DEMORALIZED
MWO
COST/ACFT
R.O.
COST/ACFT
DOLLARS PER ACFT700
600 —
500
4-00 —
300
200
1984 1994
G.M.R. 3/28/84 W.0.8402
• i ii • i ii ii i i i i i i r i 11 ii ii 11 • i 11 ii ii ii ii
MWD
COST/ACFT
WATER COST COMPARISON
IMPORTED v.s. DEMORALIZED
R.O.O ex
COST/ACFT
R.O.O BX
COST/ACFT
800
DOLLARS PER ACFT
600
400
200
10% INF1ATION
6% INFLATION
1984 1986 1988 1990 1992 1994
YEAR
C.M.R. 3/28/84 W.0.8402
1 1 ii ii ii ii it i I i i ii ii ii ii ii ii i i r i
MWD
COST/ACFT
WATER COST COMPARISON
IMPORTED v.s. DEMORALIZED
R.O. o 6X
COST/ACFT
R.O. O 8X
COST/ACFT
600
DOLLARS PER ACFT
600
400
200
6% INFLATION
STATE PROJECT ADJUSTMENT
1964 1966 1986 1990 1992 1994
YEAR
G.M.R. 3/28/84 W.0.8402
m
t.
2 DATA MCPNESENT LATEST AVAILABLE iNFONMATiON. GENERALLY SUBSEQUENT TO I»t0
) WHtRE ALINE PATT£MN REPRESENTING A FACTOR >S DASHED, TnE MATING IS
DETERMINED IT THAT FACTOR IN ADDITION TO THt tLECTBiCAL CONDUCTANCE
4 SEE APPENDIX D ?0« CHCW<CA
DATA BASCO ON SAMPLE OF ONE *CLL
COUNTY
COUNTY
GROUND MATER RATED INFERIOR BECAUSE OF NIDI
iECAuSE OF HIGH
^.-i * uRQUND *ATEH RATED iNFERiC* KCAU« OF HIGH
^fffp BORON IN ADDITION TO MiGM EtECTR.CAL CONDUCTANCE
RATING OF GROUND WATER FOR IRRIGATION USES
OTAL DISSOLVED SOUOS
J DATA REPRESENT LATEST MHtAtll INFORMATION, GENERALLY SUBSEQUENT TO I96
OETERWINCD BT THAT FACTOR IN ADDITION TO THE TOTAL DISSOLVED SOLIDS
.COUNTY
COUNTY
«AICO inrmmK MC«U« or HIGH suiraTl
GAOUNO w«Trt HVEO MARGINAL BCCAUSC Or HIGH TOTAL
DISSOLVED SOLIDS
OHND *ar[H BATED W'fRIOI* BECAUSE Or MIGM SuLfATt
IN ADDITION TO MIGM TOTAL DISSOLVED SOLIDS
CAMP
,DEL MARf /
RATING OF GROUND WATER
FOR DOMESTIC USES
V AI f nr MH. f ^
COUNTY
COUNTY
1 NUMBERS REPRESENT PREDOMINANT SUBORDINATE IONS. V' WHERE
VARIABLE
2 VALUES REPRESENT LATEST AVAILABLE INFORMATION,
GENERALLY SUBSEQUENT TO i960
3 SEC APPENDU Of OR CHEMICAL ANALYSES
VALUE BASED ON SAMPLE Of ONE WELL, SUBORDINATE IONS
CHEMICAL CHARACTER OF GROUND WATER