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SU0004912_SSNL
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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99 (STATE ROUTE 99)
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4460
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2600 - Land Use Program
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SA-99-97
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SU0004912_SSNL
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Last modified
11/19/2024 1:52:16 PM
Creation date
9/8/2019 12:59:30 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0004912
PE
2656
FACILITY_NAME
SA-99-97
STREET_NUMBER
4460
Direction
S
STREET_NAME
STATE ROUTE 99
City
STOCKTON
APN
17920032
ENTERED_DATE
3/16/2005 12:00:00 AM
SITE_LOCATION
4460 S HWY 99
RECEIVED_DATE
3/15/2005 12:00:00 AM
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
Scanner
SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\N\HWY 99\4460\SA-99-97\SU0004912\NL STDY.PDF
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EHD - Public
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D. GROUNDWATER INFORMATION <br /> Groundwater elevations are illustrated on maps published by the San Joaquin County Flood <br /> Control and Water Conservation District. The 1998 Lines of Equal Depth map denote the water <br /> table depth at approximately 70 feet below grade. The 1998 Lines of Equal Elevation indicateIII <br /> the groundwater elevation to be approximately-40 ft below mean sea level. <br /> The groundwater under the subject property may be influenced by the Little Johns Creek, <br /> adjacent to the north property border, and Highway 99. The static water level was measured <br /> within the on-site domestic well at 69 ft below the wellhead. This correlates with the Lines of <br /> Equal Depth map. As with all groundwater tables,there will be fluctuations in elevation. The <br /> 1992 Lines of Equal Elevation map indicates the groundwater table to be at-50 ft. Therefore,the <br /> water table has risen 10 ft in the last eight yrs. The critical issue regarding the groundwater <br /> elevation under the subject property is that there is sufficient distance between the floor of the <br /> 25-ft seepage pits and the highest anticipated depth to groundwater for sufficient wastewater <br /> treatment to occur. <br /> The groundwater directional flow appears to be in an easterly direction toward a zone of <br /> recharge. The water table elevation declination is relatively gradual toward this zone of recharge. <br /> The directional flow of the groundwater should be assumed to be approximate since there are <br /> many influences on flow, particularly from the Little Johns Creek. <br /> To determine the extent of nitrate impact to the underlying drinking water aquifers, a water <br /> sample was taken from the on-site domestic well for nitrate and DBCP/EDB analyses. This well <br /> is theoretically upgradient from the existing septic tank and will be theoretically crossgradient <br /> from the future leachfield and seepage pits. Test results indicate a nitrate (as NOD concentration <br /> of 7 ppm. The Maximum Contaminant Level (MCL) for nitrate (NO3) in drinking water is 45 <br /> ppm. Therefore,the nitrate impact to upgradient and underlying aquifers has been minimal. <br /> This 7 ppm concentration may be indicative of background, or naturally occurring nitrate. <br /> DBCP/EDB concentrations were Below Detection Limits (BDL), or Non-Detect (ND). <br /> E. SURFACE WATER INFORMATION <br /> Surface water impoundments for the proposed project will include a drainage/evaporation pond. <br /> This pond will be located downgradient from the leachfield and may contribute a slight dilution <br /> effect to the effluent in the top aquifer mixing layer. The Little Johns Creek is theoretically <br /> crossgradient from the leachfield area. Influence from this Creek to the leachfield area is <br /> unpredictable. <br /> 4 <br /> Va&y sig Research <br />
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