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SU0009799 SSNL
Environmental Health - Public
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SU0009799 SSNL
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Last modified
5/7/2020 11:34:14 AM
Creation date
9/6/2019 10:47:46 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0009799
PE
2656
FACILITY_NAME
PA-1200133
STREET_NUMBER
11075
Direction
W
STREET_NAME
LARCH
STREET_TYPE
RD
City
TRACY
Zip
95376-
APN
21217002
ENTERED_DATE
10/10/2013 12:00:00 AM
SITE_LOCATION
11075 W LARCH RD
RECEIVED_DATE
8/23/2012 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\L\LARCH\11075\PA-1200133\SU0009799\SS NL STDY.PDF
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EHD - Public
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05 November 2014 <br /> AGE Project No. 14-3119 <br /> Page 13 of 17 <br /> waste concentration will be between 45 mg/1-N and 85 mg/1-N; depending on the site <br /> source of the water. To prepare a conservative estimate, the concentration will be 85 <br /> mg/1-N for the restroom loading (a heavy-weighted average) loading will be used to <br /> calculate the total mg/1-N loading over a long term for subject property. The weighted <br /> average calculation for total nitrogen concentrations for on-site commercial flow is <br /> proposed as the following: <br /> • Restroom volume 5 gpd per person (99) and 3 workers per day = 510 gpd <br /> concentration will be 85 mg/1-N <br /> • Commercial concentration based on industry and SJCO EHD standards <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 leachfields 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, 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 30 percent and less desirable soils with more sands and <br /> faster percolation rates (less moisture and clay content) denitrify only about 10 percent. <br /> 9.6. MASS BALANCE OF NITROGEN LOADING <br /> The EHD requires the user to considering all potential sources identified for wastewater <br /> generation. Further the EHD supports the use of Hantzsche / Finnemore, or other <br /> appropriate formula/model to calculated a mass of nitrogen loading. <br /> Current - RESIDENTIAL <br /> The Hantzsche / Finnemore (Nr) equation for residential home application: <br /> Nr = IxNw (1-d)+ RxNb = (I+R) <br /> Nr= The average concentration of nitrate-nitrogen in the recharged waste water 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 720 <br /> gpd x 365 days of proposed operation = 262,800 gallons + 7.48 gallons per cubic foot = <br /> 35,133 cubic feet of wastewater. Does not account for evapotranspiration likely to occur. <br /> Advanced GeoEnvironmental,Inc. <br />
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