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SU0009045 SSNL
Environmental Health - Public
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SU0009045 SSNL
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Last modified
5/7/2020 11:33:50 AM
Creation date
9/4/2019 6:44:29 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0009045
PE
2626
FACILITY_NAME
PA-1200011
STREET_NUMBER
920
Direction
W
STREET_NAME
FREWERT
STREET_TYPE
RD
City
LATHROP
APN
19126022
ENTERED_DATE
1/30/2012 12:00:00 AM
SITE_LOCATION
920 W FREWERT RD
RECEIVED_DATE
1/27/2012 12:00:00 AM
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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SJGOV\rtan
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FilePath
\MIGRATIONS\F\FREWERT\920\PA-1200011\SU0009045\NL STDY.PDF
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EHD - Public
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TABLE 3 <br /> PERCOLATION TEST RESULTS FOR THE DISPOSAL AREA WITH <br /> CORRESPONDING APPLICATION RATE GALLONS/FT=/DAY <br /> 24 INCH DEEP PERC TEST BORING5.4 'n/inch / 1.086 gallons/ft/day <br /> PERCOLATION RATE/APPLICATION RATE <br /> 36 INCH DEEP PERC TEST BORING (9.4 ' inch / 1.086 gallons/f/day <br /> PERCOLATION RATE/APPLICATION RATE <br /> Awka Rah uhvftd fiom CaVbm Sime Water Rennvres Cmnot Bmd GddeRnea for ale De*n of&n v&y'memr and a based m the Pore Ram. <br /> D. GROUNDWATER INFORMATION <br /> NL 2. � SSS§4.1. Groundwater depths and elevations throughout San Joaquin County are illustrated <br /> on published by the County Flood Control and Water Conservation District. The most recent Lines <br /> of Equal Depth map(Spring 2011)do not illustrate groundwater depths in the Delta area due to shallow <br /> conditions. As noted from hand-drilling,the water table was measured at 6.75 ft below existing grade. <br /> The groundwater directional flow is generally in a northwesterly direction toward the San Joaquin River. <br /> Groundwater flow in this locale is extremely variable due to several influences such as the time of the year, <br /> surrounding irrigation, and tidal effects. <br /> SSS§2.1, 2. Since the property was intensely farmed, and since surrounding properties have also been <br /> intensely ed for several decades,the probability for high nitrate concentrations in the underlying <br /> groundwater is significant and this was observed in the water table sample. The agrichemical <br /> dibromochloropropane(DBCP)is typically analyzed for similar projects,but for this study,EHD waived <br /> testing since DBCP was never used in this locale. <br /> NLS 2.2,�;SSS§4.2. The project has an(on- ite water well for domestic purposes. There is also a <br /> I arge -si dwell that is used to su)iplmoistute for the composting piles. The following Table <br /> illustrates a nitraentrations found in each of the three sampled water sources: <br /> TABLE 4 _ <br /> WATER TABLE,DOMESTIC WELL AND IRRIGATION WELL TEST RESULTS <br /> ANALYTE WATER TABLE DO TIC WELL IRRIGATION WELL <br /> NITRATE 314 4.88 8/L 4.74 mg/L <br /> (45 =MCL) (4�in =MCL) mgLL=MCL) <br /> TOTAL ALKALINITY 439 ppm Did Not Test Did Not Test <br /> Calculation of Alkalinity Requirement for Nitrification <br /> The nitrate-nitrogen loading calculations on Page 8 are contingent upon the environmental factors required <br /> for nitrification to occur. These conditions include soil pore-space oxygen content,soil temperature,pH, <br /> electrical conductivity,organic matter,cation exchange capacity, and alkalinity. Alkalinity in wastewater <br /> effluent is derived from the encountered water table water in addition to the introduction of wastes. <br /> Nitrification consumes approximately 7.1 mg of alkalinity for every mg of ammonia-nitrogen(NH4-N) <br /> oxidized. <br /> 4 <br />
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