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SU-2601102_SSNL
Environmental Health - Public
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SU-2601102_SSNL
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Entry Properties
Last modified
2/17/2026 3:30:02 PM
Creation date
2/17/2026 3:23:48 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
File Section
COMPLIANCE INFO
FileName_PostFix
SSNL
RECORD_ID
SU-2601102
PE
2602 - SOIL SUITABILITY AND NITRATE LOADING STUDY REVIEW
STREET_NUMBER
3732
Direction
N
STREET_NAME
NEWTON
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
13206016
CURRENT_STATUS
In Review
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
3732 N NEWTON RD STOCKTON 95205
Tags
EHD - Public
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r <br /> owers are 1.8 gpm(New CA standard)and should be restricted to 10 min/shower. Assume 4 <br /> owers/day= 18 gals/shower x 4 showers/day= 72 gals/day. <br /> arrive at the yearly wastewater production, a workweek would be composed of six days, and 50 <br /> eks per year based on Holidays and other designated days off. 320 + 72 = 392 gpd x 6 d/wk x 50 <br /> s/yr= 117,600 gals/yr. This yearly wastewater generation will be used for the nitrate loading <br /> calculations below. <br /> Wastewater Characteristics <br /> The domestic wastewater generated from the office and shop buildings will be composed primarily <br /> of blackwater from toilets and graywater from hand washing. There will be no high organic loading <br /> from food preparation in a cafeteria, but additional graywater flows from showers. Consequently, a <br /> nitrogen concentration of 65 mg N/L is used below and is based on septic tank effluent analysis <br /> from similar facilities. <br /> B. CALCULATED NITRATE-NITROGEN LOADING <br /> NLS§3.0,etc. The calculated nitrate-nitrogen impact to the soil and ultimately to the groundwater is <br /> difficult to determine due to the large number of variables involved and variables unknown at this <br /> time. These include: 1.) Nitrate impact from upgradient agricultural sources, 2.) Variability in <br /> wastewater flows, effluent nitrogen concentrations and dilution effects, 3.) Changes in groundwater <br /> directional flow and elevation, 4.) The denitrification potential of the indigenous soils. <br /> HANTZ.SCHFI,G'INNEMOn,'EOUA'1'ION <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/yr <br /> Nw = Total nitrogen concentration of wastewater in mg N/L <br /> d = Fraction(%)of nitrate-nitrogen combined loss in the soil due to denitrification. <br /> R = Estimated Annual Rainfall Recharge in inches/yr. <br /> Nb = Background nitrate-nitrogen concentration of rainfall recharge, exclusive of wastewater influences. <br /> Values and Assumptions: <br /> I = 117,600 gals/-yr= 15,722 cu ft = 0.89 in/yr <br /> 4.85 ac x 43,560 sq ft/Ac x(1 ft/12 in) <br /> Page -5- <br /> Chesney Engineering, Inc. <br />
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