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SR0084717_SSNL
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Last modified
2/17/2022 12:18:44 PM
Creation date
1/13/2022 9:53:59 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0084717
PE
2602
FACILITY_NAME
285 S AUSTIN RD
STREET_NUMBER
285
Direction
S
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
22802048
ENTERED_DATE
1/12/2022 12:00:00 AM
SITE_LOCATION
285 S AUSTIN RD
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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A36 REGIONAL AQUIFER-SYSTEM ANALYSIS-CENTRAL VALLEY, CALIFORNIA <br />Valley was delineated by Berkstresser (1973). With the <br />exception of several localized pods of shallow saline <br />water, ground water in the continental and volcanic <br />deposits of the Sacramento Valley is fresh. Several <br />localized shallow saline zones were described by Berk- <br />stresser. Of these, four are now known to be underlain by <br />freshwater. These shallow saline zones, underlain by <br />freshwater, are located around the northern part of the <br />Delta, along the Sacramento River, adjacent to the <br />Sutter and Yolo bypasses, and around the base of Sutter <br />Buttes. The zone around Sutter Buttes reflects the <br />configuration of the underlying marine deposits (Berk- <br />stresser, 1973). <br />The base of freshwater as delineated by Page (1973b) <br />for the San Joaquin Valley is more complex. In the San <br />Joaquin Valley, the base of freshwater lies within the <br />unconsolidated continental deposits of Pliocene to Holo- <br />cene age, the more consolidated marine and sedimentary <br />deposits of Tertiary age, and the igneous and metamor- <br />phic rocks of pre-Tertiary age. Unlike the Sacramento <br />Valley, the base of freshwater in the San Joaquin Valley <br />is underlain by a saline water body. The depths to the <br />base of freshwater in the San Joaquin Valley range from <br />less than 100 to more than 3,500 ft below land surface. <br />DISSOLVED SOLIDS <br />The areal distribution of dissolved-solids concentra- <br />tions in ground water of the Central Valley is shown in <br />figure 24. The map for the Sacramento Valley was <br />prepared using a combination of data for dissolved solids <br />measured by the residue-on-evaporation method (72 <br />percent of the analyses) (Brown and others, 1970, p. 145) <br />and data derived from specific conductance measure- <br />ments (Fogelman, 1982a). <br />The map for the San Joaquin Valley was produced <br />primarily from dissolved-solids measurements made us- <br />ing the residue-on-evaporation method. Where data were <br />sparse, the map was modified by examining additional <br />dissolved-solids data calculated as the sum of the dis- <br />solved constituents. Because 2,000 mg/L of dissolved <br />solids is considered to be the maximum concentration in <br />freshwater (Olmsted and Davis, 1961, p. 134), only those <br />wells that yielded water with a dissolved-solids concen- <br />tration of less than 2,000 mg/L were used to prepare the <br />map. An exception to this was made along the southwest <br />margin of the San Joaquin Valley, where shallow ground <br />water has high dissolved-solids concentrations. The wa- <br />ter samples were collected between 1974 and 1982 in the <br />Sacramento Valley and between 1934 and 1985 in the San <br />Joaquin Valley. <br />Because figure 24 is a two-dimensional representation <br />of data compiled from existing wells with a wide variety <br />of depths and screen lengths, the map cannot show <br />vertical variations in water quality. It is therefore a <br />generalization of the dissolved-solids concentrations that <br />are likely to be found in a particular area, and it is most <br />representative of the ground-water zones commonly <br />used. About 11 percent of the wells in the Sacramento <br />Valley data set yielded water with dissolved-solids con- <br />centrations that were higher or lower than the mapped <br />interval. This proportion of concentrations not conform- <br />ing to mapped intervals is probably similar for the San <br />Joaquin Valley (Fogelman, 1982b). <br />The U.S. Environmental Protection Agency (1979) <br />secondary drinking-water standards recommend a limit <br />of 500 mg/L for dissolved solids. The California Domestic <br />Water Quality Regulations allow a maximum of 1,000 <br />mg/L if water of better quality is not available. However, <br />because dissolved-solids concentrations only indicate the <br />total amount of dissolved constituents in water, the <br />usability of water that exceeds 500 mg/L needs to be <br />evaluated according to the concentration of each chemical <br />constituent. <br />Dissolved-solids concentrations are lower in the north- <br />ern part and along the east side of the Central Valley. <br />Dissolved solids are higher in the south-central part of <br />the Sacramento Valley and in the western part of the San <br />Joaquin Valley. This distribution reflects the low concen- <br />trations of dissolved solids in recharge water that origi- <br />nates in the Cascade Range and the Sierra Nevada, and <br />the predominant regional ground-water flow pattern. <br />In the Sacramento Valley, dissolved-solids concentra- <br />tions generally do not exceed 500 mg/L. Two large areas <br />of shallow ground water in which concentrations of <br />dissolved solids range from 500-1,500 mg/L are present <br />in the southern part of the Sacramento Valley (fig. 24). <br />One area is south of the Sutter Buttes in the Sutter basin, <br />and the other is west of the Sacramento River extending <br />from West Sacramento on the north to the confluence of <br />the Sacramento and San Joaquin Rivers on the south (fig. <br />24). <br />In the San Joaquin Valley, dissolved-solids concentra- <br />tions are lower on the east side and higher on the west <br />side of the valley. In the center and on the east side of the <br />valley, dissolved-solids concentrations generally do not <br />exceed 500 mg/L; on the west side, most of the ground <br />water contains concentrations of dissolved solids in <br />excess of 500 mg/L. Concentrations of dissolved solids <br />generally increase to the west, and concentrations in <br />excess of 2,000 mg/L are not uncommon along the west <br />margin of the valley. <br />HYDROCHEMICAL FACIES <br />Where a few ions dominate the dissolved-solids content <br />of ground water, the term "hydrochemical fades" (Back, <br />1961) is used to describe the dominant ion patterns. The
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