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SR0080912 SSNL
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SR0080912 SSNL
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Last modified
2/10/2022 2:11:11 PM
Creation date
12/4/2019 8:50:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0080912
PE
2602
STREET_NUMBER
3732
Direction
E
STREET_NAME
CARPENTER
STREET_TYPE
RD
City
STOCKTON
Zip
95215
APN
17916050
ENTERED_DATE
7/18/2019 12:00:00 AM
SITE_LOCATION
3732 E CARPENTER RD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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`7� 777� <br /> B, CALCULATED NITRATE-NITROGEN LOADING <br /> NLS§3.4,3.5,3.6. The calculated nitrate-nitrogen impact to the soil and ultimately to the <br /> groundwater is difficult to determine due to the large number of variables involved and variables <br /> unknown at this time. These include: 1.) Impact from upgradient nitrate sources, 2.)Variability <br /> in wastewater flows, effluent nitrogen concentrations and dilution effects from stormwater <br /> recharge, 3.) Changes in groundwater directional flow and elevation, 4.)And of significant <br /> importance is not only the denitrification potential of the indigenous clays, but equally important <br /> is the diminished nitrification potential within the clay soil environment. The extremely small <br /> pore space within the high clay content soil significantly reduces oxygen content,thus impeding <br /> nitrification. <br /> The Hantzsche/Finnemore Formula is used below to predict the average resultant concentration of <br /> nitrate-nitrogen in effluent recharge water from the proposed wastewater treatment and effluent <br /> management system serving the proposed Heaven Temple. The calculations are based on a total <br /> areal loading from the entire Parcel, because all three contribute nitrogen sources from residential, <br /> the existing Temple and the future Temple, all correlated with the annually projected wastewater <br /> flows of 971,712 gpy as calculated above. <br /> CALCULATED NITRATE-NITROGEN LOADING FROM THE COMBINED PRESENT AND <br /> FUTURE WASTEWATER FLOW VOLUMES FOR THE ENTIRE SUBJECT PARCEL: <br /> HANTZSCHEIFINNEMORE EQUATION <br /> INWLL-d)+RNb <br /> Nr= (I+R) <br /> Where: <br /> Nr = Resultant average concentration of nitrate-nitrogen in recharge water-(ppm NO3-N) <br /> I = Volume rate of wastewater entering the soil averaged over the gross developed area in inches per yr <br /> Nw = Total nitrogen concentration of wastewater in mg N/L <br /> d = Fraction(%)of nitrate-nitrogen combined loss in the high clay content soil due to: <br /> 1.) Prevention of nitrification and 2.)The denitrification of nitrate molecules that may form. <br /> R = Average recharge rate of rainfall-inches per yr NLS§3.2 <br /> Nb = Background nitrate-nitrogen concentration of rainfall recharge,exclusive of wastewater influences <br /> (ppm NO3-N). <br /> Values and Assumptions: <br /> I=971,712 sals=total WW/yr=129,908 cu ft = 1.157 in/yr <br /> 30.94 Ac x 43,560 sq ft/Ac x(1 ft/12 in) <br /> Nw= 90 mg N/L <br /> d = Assume 25%due to the high percentage of clay soil(29%)throughout the soil profile that not only <br /> mitigates nitrification,but also promotes denitrification of nitrate molecules that may form. <br /> Page-8- <br /> Chesney Consulting <br />
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