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SR0082741_SSNL
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2600 - Land Use Program
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SR0082741_SSNL
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Last modified
11/23/2020 9:22:36 AM
Creation date
11/23/2020 9:14:14 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0082741
PE
2602
FACILITY_NAME
HARNEY LANE PROPERTY
STREET_NUMBER
23649
Direction
E
STREET_NAME
HARNEY
STREET_TYPE
LN
City
LODI
Zip
95240
APN
06704009
ENTERED_DATE
10/15/2020 12:00:00 AM
SITE_LOCATION
23649 E HARNEY LN
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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new method to determine flow from residential sources. He indicated that wastewater <br /> flow from a single-family residence should be calculated as 100 gallons per day (gpd) <br /> for the first bedroom and 50 gpd for each additional bedroom; additional residences <br /> should be calculated in the same manner (personal communication, March 4, 2020). <br /> The first hypothetical house on each parcel will have five bedrooms, which would result <br /> in a flow value of 300 gpd using the new method. The second hypothetical house will <br /> have three bedrooms, which would result in a flow value of 200 gpd. The maximum <br /> daily flow for each parcel is thus estimated to be 500 gpd. <br /> A typical residential concentration of 35 mg/L of nitrate as N was selected for the <br /> proposed residences (Crites and Tchobanoglous, 1998). <br /> The estimated flow values discussed here should not be used for the design and sizing <br /> of the septic system. The design and sizing of the septic system should utilize the San <br /> Joaquin County Environmental Health Department On-Site Wastewater Treatment <br /> Systems Standards which incorporate peak and surge flow factors. The estimates used <br /> in the On-Site Wastewater Treatment Systems Standards may be greater than those <br /> discussed here. <br /> Denitrification Reductions <br /> Denitrification is a process that occurs in the septic system drain field whereby certain <br /> bacteria oxidize the nitrate (NO3) in the wastewater and release nitrogen gas (N2) to the <br /> atmosphere. Due to the biologic processes in the shallow soils, nitrogen in the drain <br /> field may undergo a reduction between 10 percent to 35 percent. Soils with higher clay <br /> content, moist soil conditions, high pH, and organic material denitrify by about 35 <br /> percent, and soils with high sand content tend to denitrify at a lower rate of about 10 <br /> percent. <br /> A denitrification factor of 35 percent was selected for Parcels 1, 3, 4, 5, and 8 of the Site <br /> because of the clayey soil present at the percolation test locations. A standard <br /> denitrification factor of 25 percent was selected for Parcels 2, 6, and 7 of the Site <br /> because of the sand/silt mixtures present at the percolation test locations. <br /> Nitrate Loading Estimate <br /> Two nitrate loading scenarios were employed for each proposed parcel to <br /> determine the impact from the project to ground water: one scenario assuming <br /> no future development, and one scenario assuming the hypothetical future <br /> homes discussed above. The scenarios utilize the variables discussed previously, <br /> which represent the estimated conditions and uses associated with this project. The <br /> nitrate loading calculations are presented in Plates 23 through 30. <br /> LOGE 20-29 Page 13 <br />
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