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SR0083203_SSNL
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SR0083203_SSNL
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Last modified
2/17/2021 2:17:26 PM
Creation date
2/17/2021 2:04:35 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SR0083203
PE
2602
FACILITY_NAME
6631 S JACK TONE RD
STREET_NUMBER
6631
Direction
S
STREET_NAME
JACK TONE
STREET_TYPE
RD
City
STOCKTON
Zip
95215
APN
18108017
ENTERED_DATE
1/25/2021 12:00:00 AM
SITE_LOCATION
6631 S JACK TONE RD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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AdvancedGeo <br />20 January 2021 An Employee -Owned Compony <br />Project No. 20-6284 <br />Page 12 of 14 <br />9.5. DENITRIFICATIONS CAUSED BY SOILS <br />The process of denitrification is important when utilizing subsurface septic lines and <br />regularly occurs in the soil within the leach fields where bacteria utilize oxygen in the <br />nitrate to release nitrogen gas out to the atmosphere. The denitrification process is <br />controlled by waste concentrations, soil type, annual rainfall, pH of the soils, total organic <br />concentration of the soil (TOC) and exposure time to nitrogen. The soils with a high or <br />moderate clay content, higher organic content, high pH, and adequate soil moisture <br />denitrify the concentrations by approximately 30 percent and less desirable soils with <br />more sands and faster percolation rates (less moisture and clay content) denitrify only <br />about 10 percent. A denitrification factor of 30 percent was selected for the calculation <br />based on the silty clay loam soil existing at the site. <br />9.6. MASS BALANCE OF NITROGEN LOADING <br />The EHD requires the user to consider all potential sources identified for wastewater <br />generation. Further, the EHD supports the use of Hantzsche/Finnemore, or other <br />appropriate formula/model to calculate a mass of nitrogen loading. <br />RESIDENTIAL: <br />The Hantzsche / Finnemore (Nr) equation for residential home application: <br />Nr=IxNw(1-d)+RxNb=(I+R) <br />n,nfinitinns- <br />Nr = The average concentration of nitrate -nitrogen in the recharged wastewater parts per <br />million of nitrate -nitrogen. <br />I = Volume rate of wastewater entering the soil averaged over the gross developed area <br />(acres) in inches per year. The total wastewater volume for proposed project will be <br />200 gpd (proposed system) x 365 days of proposed operation = 200 x 365 days T 7.48 <br />gallons per cubic foot = 9,759 cubic feet of wastewater. Does not account for <br />evapotranspiration likely to occur. <br />NW = Total nitrogen concentration of wastewater at 45 mg/L-N based on the average <br />discharge. Accounting for the loss of mg/L-N in the septic tank at 15% = 45-15%= 38.25 <br />and the loss from the biomat at 10% 38.25 - 10% = 34.425 mg/L-N. <br />d = Fraction of nitrogen concentration removed from the wastewater due to denitrification <br />within the soil (30 percent for silty clay loam soils). <br />R = Estimated Deep percolation / average rainfall recharge rate per year: 3.69 inches. <br />
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