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SU-2601254_SSNL
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Entry Properties
Last modified
4/15/2026 8:38:38 AM
Creation date
4/15/2026 8:36:22 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU-2601254
PE
2602 - SOIL SUITABILITY AND NITRATE LOADING STUDY REVIEW
STREET_NUMBER
202
Direction
W
STREET_NAME
MATHEWS
STREET_TYPE
RD
City
FRENCH CAMP
Zip
95231
APN
19319014
CURRENT_STATUS
In Review
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
202 W MATHEWS RD FRENCH CAMP 95231
Tags
EHD - Public
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III. NITRATE LOADING STUDY FINDINGS <br /> A. WASTEWATER FLOW VOLUME PROJECTIONS AND CHARACTERISTICS <br /> Wastewater Flow Volume Projections <br /> To determine nitrate-nitrogen loading from any project, wastewater flow volumes must be <br /> determined as accurately as possible. The future Restroom building is assumed to be a Men's and <br /> Women's Restroom with toilets, urinals and lavatories. <br /> A toilet flush+hand washing total approx. 1.78 gallons (1.28 gals-New CA standard)+0.5 = 1.78 gals) <br /> Assume there are on average three flushes each hour, for two toilets+lavatories, 8 hrs per day: <br /> 1.78 gals/toilet flush x 3 flushes/hr x 8 hrs/day x 2 toilets= 85 gpd ADF x 365 d/y= 31,025 gpy. <br /> Alternatively, a proposed demographic of 15 people are assumed to be onsite daily: <br /> 15 people (per the CDD CUP) x 1.78 gals/toilet flush = 27 gpd ADF x 365 d/y= 9,746 gpy. <br /> The more conservative factor of 31,025 gpy will be used in the nitrate loading calculations below. <br /> Wastewater Characteristics <br /> The domestic wastewater generated from the restroom building will be composed primarily of <br /> blackwater from toilets and graywater from hand washing. There will be no high organic loading <br /> such as food preparation in a cafeteria. Consequently, a nitrogen concentration of 90 mg N/L is <br /> used below and is based on septic tank effluent analysis from similar facilities. <br /> B. CALCULATED NITRATE-NITROGEN LOADING <br /> NLS§3.0. 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 /> HAN17SCHFIFINNEMORE SQUAT/ON <br /> IN,,,0 -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 NO3-N concentration of rainfall recharge, exclusive of wastewater influences. <br /> Page -4- <br /> Chesney Engineering, Inc. <br />
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