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SU0009972 SSNL
Environmental Health - Public
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SU0009972 SSNL
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Last modified
5/7/2020 11:34:19 AM
Creation date
9/5/2019 11:19:53 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0009972
PE
2631
FACILITY_NAME
PA-1400042
STREET_NUMBER
9851
Direction
E
STREET_NAME
HUTCHINSON
STREET_TYPE
RD
City
MANTECA
Zip
95336-
APN
25724048
ENTERED_DATE
3/4/2014 12:00:00 AM
SITE_LOCATION
9851 E HUTCHINSON RD
RECEIVED_DATE
3/3/2014 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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FilePath
\MIGRATIONS\H\HUTCHINSON\9851\PA-1400042\SU0009972\NL STDY.PDF
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EHD - Public
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TABLE 3 <br /> TEST RESULTS FOR THE ON-SITE DOMESTIC WELL <br /> ANALYTE ON-SITE DOMESTIC WELL <br /> Nitrate(As nitrate) 17.4 mg/L <br /> DBCP ND <br /> Dibromochloropropane Non Detect <br /> Alkalinity 100 mg/L <br /> Calculation of Alkalinity Requirement for Nitrification <br /> The nitrate-nitrogen loading calculations on Page 8 are contingent upon the environmental factors <br /> required for nitrification to occur. These conditions include soil pore-space oxygen content, soil <br /> temperature, pH, electrical conductivity, organic matter, cation exchange capacity, and alkalinity. <br /> Alkalinity in wastewater effluent is derived from the domestic well water supply in addition to the <br /> introduction of human wastes. Nitrification consumes approximately 7.1 mg of alkalinity for every <br /> mg of ammonia-nitrogen (NH4 N)oxidized. Nitrification of the average Total Nitrogen(TN) <br /> concentration of 82 mg/L, as determined on Page 8 would require: 82 mg/L NH4-N x 7.1 mg <br /> CaCO3= 582 mg/L alkalinity. The alkalinity in the domestic well water supply was measured at <br /> 100 mg/L. The alkalinity of the wastes is unknown, but the combination of the well water and <br /> wastes would most likely be below 582 mg/L which would thus inhibit nitrification to an <br /> indeterminable degree. <br /> E. SURFACE WATER INFORMATION <br /> Storm water management will consist of runoff into the adjacent kiwi orchard directly to the north <br /> of the facility. A Stormwater Pollution Prevention Plan (S WPPP) is being developed for this <br /> project. Percolating stormwater may produce dilution effects to the underlying water table. <br /> Groundwater dilution effects can only be truly discerned with groundwater monitoring and <br /> modeling. According to a scientific paper authored by Shaw and Turyk (1994),reduction of nitrate <br /> concentrations in groundwater can occur primarily through dispersion, or by percolating rainwater, <br /> or a water source including effluent water recharge. <br /> Climatic Data: Rainfall versus Evapotranspiration <br /> NLS§3.2. It is generally and scientifically accepted that when precipitation exceeds <br /> evapotranspiration(Eto), deep percolation of surface rainwater may occur. Evapotranspiration <br /> refers to water evaporation that takes place both at the soil surface and transpiration by plants. The <br /> following Table illustrates rainfall and evapotranspiration for the Tracy area(closest data available). <br /> Precipitation data was obtained from the Soil Survey of San Joaquin County. The conservative"2 <br /> years in 10" data was used and not the "average rainfall"data. Evapotranspiration data was <br /> obtained from the California Irrigation Management Information System(CIMIS): <br /> 5 <br />
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