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COMPLIANCE INFO_NL STDY
Environmental Health - Public
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WALNUT GROVE
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4200 – Liquid Waste Program
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PR0522382
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COMPLIANCE INFO_NL STDY
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Last modified
12/3/2020 5:09:47 PM
Creation date
8/5/2020 10:12:35 AM
Metadata
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Template:
EHD - Public
ProgramCode
4200 – Liquid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
NL STDY
RECORD_ID
PR0522382
PE
4242
FACILITY_ID
FA0014762
FACILITY_NAME
JD Service Station, Inc.
STREET_NUMBER
9015
STREET_NAME
WALNUT GROVE
STREET_TYPE
RD
City
THORNTON
Zip
95686
CURRENT_STATUS
01
SITE_LOCATION
9015 WALNUT GROVE RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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\MIGRATIONS\4200 - Liquid Waste\W\WALNUT GROVE\9015\PR0522382\NL STDY.PDF
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EHD - Public
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Mr.Jadi Singh L..i <br /> February 11,2003 <br /> Page 3 <br /> Variables and Assumptions <br /> Denitrification is one of many important processes occurring in septic system tanks and leachfields <br /> whereby certain bacteria utilize the oxygen in the nitrate(NOO and release nitrogen gas (N2)to the <br /> atmosphere. Denitrification is expressed as a percentage, and the normally accepted range is 10 percent <br /> to 35 percent. Soils with higher clay content, moist soil conditions, high pH, and organic material <br /> denitrify about 35 percent of effluent. Soils with very high sand content and fast percolation rates are <br /> estimated to denitrify effluent at a lower rate, about 10 percent to15 percent(Hantzshe and Finnemore, <br /> 1991). Due to the presence of highly permeable sandy soils,the denitrification factor is estimated to be <br /> 10 percent. <br /> An estimate of the quantity and quality of rainfall and effluent is required for the analysis. The C1M1S <br /> agricultural information was accessed on the internet for average monthly rainfall and average monthly <br /> evapotranspiration (ET) for the Lodi West no. 166 weather station(http//www.cimis.water_ca.gov/). <br /> Rainfall average for the Lodi station is given in the San Joaquin County Soil Survey(SCS, 1992). The <br /> calculation and assumptions discussed on Plate No. 1, indicate deep percolation of rain in Lodi was <br /> estimated to be 7.28 inches. The nitrate concentration of rain fall was estimated to be 1 m /L-N <br /> (Hantzshe and Finnnemo,1991). <br /> The quantity waste water was estimated to be 3,000 gallons per day(gpd). The average nitrate <br /> concentration of a MicroSepTee treatment system averages less than 10 mg/L-N. The United States <br /> Environmental Protection Agency (EPA)maximum contaminate level for drinking water is 10 mg/L-N <br /> nitrate. Raw septic waste is normally considered to range between 20 to 100 mg/L-N total nitrogen with <br /> normal residential use averaging between 35 to 45 mg/L-N total nitrogen. <br /> As a result of the analysis, the use of the engineered septic system should not cause a build up of nitrates <br /> above the EPA maximum contaminate level for nitrates in drinking water of 10 mg/L-N. The Ne value or <br /> average concentration of percolating effluent is 6.9 mg/L-N. Please see Table 2 for a summary of the <br /> calculation and Plate No. 2 for the calculation. <br /> Table 2. <br /> Summary of Nitrate Mass Balance Analysis. <br /> Type of facility, *Result: Denitrification Deep Waste Parcel Rain <br /> maximum flow Nitrate FactorRain Level to Size Concentrat- <br /> Concentration Percol- Septic (ac) ion <br /> ation Tank' <br /> Gas 6.9 mg/L-N 10% 7.28 10 mg/L- 2.0 1 mg/L-N <br /> Station/Convenien inches N <br /> cc Store,3,000 <br /> gpd• <br /> *Note: Maximum contaminate level for Nitrate is 10 mg/L-N(45 mg/L as NO,). <br /> �gERso� i <br /> P <br /> Y W <br /> o . <br />
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