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SR0079389 SSNL
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Last modified
1/15/2020 2:30:27 PM
Creation date
9/4/2019 11:12:14 AM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0079389
PE
2601
STREET_NUMBER
17386
Direction
N
STREET_NAME
CHERRYWOOD
STREET_TYPE
ST
City
VICTOR
Zip
95253
APN
05110012
ENTERED_DATE
7/12/2018 12:00:00 AM
SITE_LOCATION
17386 N CHERRYWOOD ST
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\sballwahn
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FilePath
\MIGRATIONS\C\CHERRYWOOD\17386\NL STUDY.PDF
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EHD - Public
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Nitrate Loading Study Irerracon <br /> Roque Property e Victor, California <br /> July 6, 2018 e Terracon Project No. NA187032 <br /> potential sewage flow rate for both the existing and proposed future site use is 560-gallons per <br /> day. <br /> The average total nitrogen concentration of domestic wastewater is normally considered to be 20 <br /> to 85 mg/L-N with 35 to 45 mg/L-N being typical (Crites and Tchobanoglous, 1998). It is estimated <br /> that commercial use will have higher concentrations of total nitrogen when compared to residential <br /> use. For the purposes of the nitrate loading estimate, it is estimated that the average <br /> concentration for total nitrogen in wastewater for the project is approximately 35 mg/L-N over the <br /> long term. <br /> 3.5.1 Denitrification Estimate <br /> Denitrification is an important process which occurs within the leach field whereby certain bacteria <br /> utilize the oxygen in the nitrate (NO3) and release nitrogen gas (N2) to the atmosphere. <br /> Denitrification is expressed as a percentage, and the normally accepted range is 10 percent to 35 <br /> percent. Soils with higher clay content, moist soil conditions, high pH, and organic material <br /> denitrify by about 35 percent, and soils with high sand content and fast percolation rates are <br /> estimated to denitrify at a lower rate, about 10 to 15 percent. Based on the USDA soil survey <br /> (Section 1.1), Tokay fine sandy loam soils are anticipated at the site, depth to groundwater of 80 <br /> to 120 feet bgs, and the potential for interstratified finer grained soils to exist between the upper <br /> sandy loam and groundwater that are anticipated at the site with some layers of hardpan; a <br /> denitrification factor of 25 percent was selected. <br /> 3.5.2 Nitrate Loading Scenario <br /> The following table presents a summary of the nitrate loading calculation for the proposed site <br /> use. A copy of the nitrate loading calculation is included in Appendix B. <br /> Table 3. <br /> Summary of Nitrate Mass Balance Equation. <br /> Result Effluent Deep <br /> Average Leachfield <br /> Land Use (Nc)* Acres (A) Daily Flow Concentration Denitrification Percolation <br /> (mg/L- (a)(gpd) (Nw) (d) of Rainfall <br /> N) (mg/L-N) (R) (in) <br /> Proposed 24.0 0.13 560 35 25% 5.76 <br /> residential use <br /> * Maximum contaminant level (MCL)for nitrate in drinking water is 10 mg/L-N. <br /> Based on the nitrate loading balance calculation (Table 3), nitrate levels for the proposed future <br /> use is anticipated to be 24.0 mg/L-N which is above the MCL of 10.0 mg/L-N. <br /> Responsive■ Resourceful ■ Reliable 7 <br />
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