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SR0082543_SSNL
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2600 - Land Use Program
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SR0082543_SSNL
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Entry Properties
Last modified
11/20/2020 8:13:58 AM
Creation date
10/12/2020 10:51:13 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0082543
PE
2602
STREET_NUMBER
122
Direction
W
STREET_NAME
HARNEY
STREET_TYPE
LN
City
LODI
Zip
95245
APN
05806046
ENTERED_DATE
9/2/2020 12:00:00 AM
SITE_LOCATION
122 W HARNEY LN
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Revised November 4, 2020 <br /> BGG Job No. G164.01 <br /> an agricultural worker; this rate was used for the nurdery employees. The estimated flow values <br /> discussed here should not be used for the design and sizing of the septic system. The design and <br /> sizing of the septic system should utilize the San Joaquin County Environmental Health Department <br /> On-Site Wastewater Treatment Systems Standards which incorporate peak and surge flow factors. <br /> The estimates used in the On-Site Wastewater Treatment Systems Standards may be greater than <br /> those discussed herein. <br /> The nitrate as nitrogen (N) concentration for non-showering employee use is estimated to be 85 <br /> mg/L (US EPA, 1980). This value was used in calculations for the nursery employees. No <br /> contributions from crop irrigation or soil amendments are considered for the Hantzsche/Finnemore <br /> method.It is reasonably assumed that the irrigation and soil amendments would be applied at close <br /> to agronomic rates for a net balance of plant irrigation and nutrients. The following tables present <br /> the calculated maximum average daily flow for the site and weighted average concentrations: <br /> Table 1 —Average Daily Flow Calculation <br /> Use Units Rate Subtotal Reduction' Average <br /> Daily Flow <br /> Employees full-time 50 15 gal/employee 750 gpd 5/7 535.7 gpd <br /> Total 535.7 gpd <br /> 1 Reduction factors convert calculated flow into average daily flow over a one-year period; 517 converts for <br /> anticipated weekday operations. <br /> Table 2—Weighted Avera a Concentration Calculation <br /> Use Average Daily Flow Estimated Waste Weighted Average <br /> Water Quality Product <br /> Employees 535.7 gpd 85 mg/L-N 45,535.7 gpd-mg/L-N <br /> full-time <br /> Totals 535.7 gpd 45,535.7 gpd-mg/L-N <br /> Weighted Average 45,535.7 gpd-mg/L-N/535.7 gpd= 85 mg/L-N <br /> Concentration: <br /> Denitrification Reductions <br /> Denitrification is a process that occurs in the septic system drain field whereby certain bacteria <br /> oxidize the nitrate(NO3)in the wastewater and release nitrogen gas(N2)to the atmosphere. Due to <br /> the biologic processes in the shallow soils, nitrogen in the drain field may undergo a reduction <br /> between 10 percent to 25 percent. Soils with higher clay content,moist soil conditions,high pH,and <br /> organic material denitrify by about 25 percent,and soils with high sand content and fast percolation <br /> rates tend to denitrify at a lower rate of about 10 percent. A typical denitrification factor of <br /> 15 percent was estimated for the site due to the presence of cemented hardpan lenses below 4 feet <br /> deep at the site. <br /> Nitrate Loading Estimate <br /> A nitrate loading scenario was employed to determine the impact from the proposed project to <br /> groundwater. The scenario utilizes the variables discussed previously,which represent the estimated <br /> conditions and uses associated with this project. The following table presents a summary of the <br /> assumptions for the nitrate loading calculation for the site. <br /> BAEZ GEOTECHNICAL GROUP Soil Suitability Study and Nitrate Loading Study-I Hsin Orchids Pagel <br />
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