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SR0085397_SSNL
Environmental Health - Public
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SR0085397_SSNL
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Last modified
7/8/2022 9:39:41 AM
Creation date
6/30/2022 1:17:16 PM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0085397
PE
2602
STREET_NUMBER
23751
Direction
S
STREET_NAME
BIRD
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
25010015
ENTERED_DATE
6/13/2022 12:00:00 AM
SITE_LOCATION
23751 S BIRD RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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1.5 gals/flush(1.0 gals flush+0.5 hand washing)x 4 flushes/hr x 10 hr/day= 60 gpd <br /> Three sinks are proposed: 0.5 gals/use x 50 uses/day =25 gpd <br /> Totals= 160 +60 +25 =245 gpd=Average Daily Flow(ADF). <br /> 245 gpd x six days/wk x 52 wk/yr= 76,440 gals/yr. This figure will be used in the nitrate loading <br /> calculations below and fore design purposes. <br /> Wastewater Characteristics <br /> The domestic wastewater generated from the Office Building will be composed of blackwater from <br /> toilets and graywater from hand washing. There will be no high organic loading from kitchen use, <br /> etc. Additionalvastewater constituents may consist of other liquids to the system, such as coffee, <br /> juices, low strength cleaning liquids, etc. No industrial or commercial chemicals, solvents, etc. <br /> should ever be introduced into the wastewater treatment system. It is imperative that low strength <br /> and low volumes of cleaners are used in the restroom since they can disrupt the septic tank biology. <br /> A value of 90 mg N/L is typically used for commercial wastewater calculations. <br /> i <br /> B. CALCULATED NITRATE-NITROGEN LOADING <br /> NLS§3.4,3.5,3.6. The calculated nitrate-nitrogen impact to the soil and potentially 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 in <br /> wastewater flows, effluent nitrogen concentrations and dilution effects from rainfall recharge, 3.) <br /> Changes in groundwater directional flow and elevation. <br /> The Hantzsche/Finnemore Formula is used below to predict the average concentration of nitrate- <br /> nitrogen in effluent recharge water from the proposed OWTS and existing modular home. The <br /> calculations are based on a total areal loading basis of 21.83 acres, correlated with the annually <br /> projected wastewater flows of 76,440 gpy for the modular Office Building. These two factors <br /> primarily estimate the average concentration of nitrate-nitrogen in the recharge effluent, which <br /> should not exceed 10 ppm nitrate-nitrogen(45 ppm as nitrate). <br /> IN,„G - d, +R Nb <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 denitrified. <br /> R See Section II E,Page 4 <br /> Nb = Background nitrate-nitrogen concentration of rainfall recharge, exclusive of wastewater influences <br /> (ppm NO3-N). <br /> e -6- <br /> Chesney Consulting <br />
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