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SU0006343 SSNL
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SU0006343 SSNL
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Last modified
5/7/2020 11:32:20 AM
Creation date
9/4/2019 11:22:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0006343
PE
2632
FACILITY_NAME
PA-0600630
STREET_NUMBER
11770
Direction
W
STREET_NAME
CLOVER
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
21226019
ENTERED_DATE
12/12/2006 12:00:00 AM
SITE_LOCATION
11770 W CLOVER RD
RECEIVED_DATE
12/12/2006 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\C\CLOVER\11770\PA-0600630\SU0006343\NL STDY.PDF
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EHD - Public
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rT7atalrogen is the summation of ammonia-nitrogen (NH4) and organic nitrogen(proteins, amino <br /> acids, enzymes). Since the septic tank is predominately anaerobic, nitrogen cannot exist in its <br /> oxidized state as nitrate for any length of time in the septic effluent, and if it does, it is quickly <br /> reduced to NO or NOz. If nitrate existed in the tank effluent, this would also be added to ammonium <br /> and organic nitrogen to arrive at Total Nitrogen. <br /> NLS§ .33 <br /> : To quantify the anticipated nitrogen concentration for use in the nitrate loading <br /> calculations for this project, effluent sample test results were obtained from three other Places of <br /> Worship in San Joaquin County. These analytical test results were averaged to provide the <br /> concentrations found in Column 2, in Table 7 below. <br /> In addition, septic tank effluent concentrations from various researchers that have been published in <br /> Small and Decentralized Wastewater Management S, sty ems,by Crites and Tchobanoglous are found <br /> in Columns 3 and 4. These two columns illustrate the effect effluent filtration has on certain <br /> constituents of the effluent, particularly BOD and TSS. Column 5 illustrates septic tank effluent <br /> concentrations for the constituents listed that have been determined by the U.S.E.P.A. <br /> TABLE 7 <br /> 4Analysis of Septic" Critcs and. Crites and u.5.t✓.P.A. <br /> ANALYTE System Effluent; Tchobauoglousc .460anoglous: <br /> Averaged From With Effluent Filter Without Effluent Filter <br /> Three S.J:C. <br /> Churches.. <br /> Ammonia Nitrogen(NH.-N) 103 mg/L 40 mg/L 40 mg/L 6-18 mg/L <br /> Organic Nitrogen 10 mg/L 28 mg/L 28 mg/L 30-82 mg/L <br /> Nitrate BDL BDL BDL BDL <br /> Total Nitrogen (TN) 113 mg/L 66 mg/L 68 mg/L 35-100 mg/L <br /> Total Suspended Solids 72 mg/L 80 mg/L 30 mg/L 200-290 mg/L <br /> (TSS) <br /> Biochemical Oxygen 21 mg/L 180 mg/L 130 mg/L 200-290 mg/L <br /> Demand(BODS) <br /> pll 7.7 N/A NIA NIA <br /> Total Alkalinity 983 mg/L 60-120 mg/L 60-120 mg/L N/A <br /> B. CALCULATED NITRATE-NITROGEN LOADING <br /> NLS§3.3: The calculated or estimated nitrate-nitrogen impact to the soil and ultimately to the <br /> groundwater is difficult to determine due to the number of variables involved. These variables <br /> include 1.) Variability in wastewater flows leading to variability in nitrogen concentrations and <br /> dilution effects that may occur, 2.) Impact from previous on-site poultry operations, 3.)Upgradient <br /> nitrate sources from agricultural farmland,4.) Changes in groundwater directional flow and elevation, <br /> 5.)Denitrification potential of the underlying soil, and 5.) Rainfall recharge. <br /> 13 <br /> ChesneyConsulting <br /> r g <br />
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