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SR0085800_SSNL
Environmental Health - Public
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2600 - Land Use Program
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SR0085800_SSNL
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Last modified
9/30/2022 8:29:54 AM
Creation date
9/30/2022 8:23:55 AM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0085800
PE
2602
STREET_NUMBER
12960
Direction
E
STREET_NAME
JAHANT
STREET_TYPE
RD
City
ACAMPO
Zip
95220
APN
00727022
ENTERED_DATE
9/20/2022 12:00:00 AM
SITE_LOCATION
12960 E JAHANT RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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12958/12970 E Jahant Road Project No. 2022-00037 Page 17 <br />For the site, the total daily toilet use contributing wastewater quantity, considering the <br />existing and planned residential dwellings is 750 gallons per day. The average total nitrogen <br />concentration of domestic wastewater is normally considered to be 20-85 mg/L-N with 35 <br />to 45 mg/L-N being typical (Crites and Tchobanoglous, 1998). Based on EHD request with <br />previous studies, it is estimated that residential domestic wastewater concentration will be <br />approximately 35 mg/L-N. <br />5.4.2 Denitrification Estimate <br />Denitrification is an important process which occurs within the leach field whereby certain <br />bacteria utilize the oxygen in the nitrate (NO3) and release nitrogen gas (N2) to the <br />atmosphere. Denitrification is expressed as a percentage, and the normally accepted range <br />is 10 percent to 35 percent. Soils with higher clay content, moist soil conditions, high pH, <br />and organic material denitrify by about 35 percent, and soils with high sand content and fast <br />percolation rates are estimated to denitrify at a lower rate, about 10 percent to 15 percent. <br />Although there was clay and hardpan observed at the shallow percolation test layer, a sandy <br />loam layer was observed from approximately 8 feet to 12.25 feet below ground surface. <br />Based on the fine sandy loam soil type for the subject property, denitrification is estimated <br />to be 25 percent. <br />5.5 Nitrate Loading <br />A nitrate loading scenario was performed to determine the impact from the proposed <br />project. The scenario utilizes the variables discussed previously which represent the <br />estimated conditions and uses associated with this project. The following table presents a <br />summary of the nitrate loading calculation for the parcel. <br />Table 4. <br />Srnmmnry of Nitrate MaCC Ralance Analvsis_ <br />Parcel <br />Result <br />Acres <br />Average Daily Flow <br />Effluent <br />Leachfield <br />Deep Percolation <br />(Nc) * <br />(A) <br />(Q) <br />Concen- <br />Denitrifi- <br />of Rainfall (R) <br />(mg/L-N) <br />(gpd) <br />tration (Nw) <br />cation (d) <br />(Plate 7) (in.) <br />(mg/L-N) <br />1 <br />8.4 <br />4.59 <br />750 <br />35.00 <br />25% <br />5.29 <br />* Maximum contaminant level (MCL) for nitrate in drinking water is 10 mg/L-N. <br />5.6 Impact of Nitrate Loading to Nearby Water Sources <br />The nitrate maximum contaminant level (MCL) set by the US EPA is 45 mg/L-NO3 or <br />10 mg/L-N. Based on the methods and assumptions described, the project will result in <br />nitrate 8.4 mg/L-N. The depth to groundwater for this site is approximately 155 to 160 feet <br />below ground surface. Based on the mass balance analysis results, in addition to our <br />professional judgement, low septic tank density, and geologic setting showing the deep <br />groundwater table underlying the Site, we believe the proposed project will not likely cause <br />a build-up of nitrate in the ground water above the background concentration of total <br />Petralogix Engineering, Inc. <br />26675 Bruella Road, Galt, Ca 95632 <br />(209)-400-5729 <br />www.petraloglx.com <br />
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