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SU0008552 SSNL
Environmental Health - Public
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SU0008552 SSNL
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Last modified
5/7/2020 11:33:33 AM
Creation date
9/4/2019 6:34:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0008552
PE
2631
FACILITY_NAME
PA-1000277
STREET_NUMBER
4715
Direction
E
STREET_NAME
FOPPIANO
STREET_TYPE
LN
City
STOCKTON
APN
08531012
ENTERED_DATE
12/21/2010 12:00:00 AM
SITE_LOCATION
4715 E FOPPIANO LN
RECEIVED_DATE
12/17/2010 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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\MIGRATIONS\F\FOPPIANO\4715\PA-1000277\SU0008552\NL STDY.PDF
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EHD - Public
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III. NITRATE LOADING STUDY FINDINGS <br /> A. WASTEWATER CHARACTERISTICS AND FLOW VOLUME PROJECTIONS <br /> WASTEWATER CHARACTERISTICS <br /> Because there will be a kitchen adjoining the Temple/Prayer Hall, there may be additional organic <br /> loading. However,this organic loading should be low since the foods prepared are not greasy or <br /> oily. All food wastes must be handled as a solid waste to reduce organic loading. Additionally, <br /> there will be very little dishwashing since all utensils will be disposable. Of a higher consequence, <br /> is that a percentage of the wastewater flows will be wash water. This graywater will be from the <br /> washing of feet and will have low nitrogen concentrations. The wash area is denoted on the <br /> Architectural Plans as"Feet Wash Area." <br /> C3 �� Therefore, the two graywater sources of kitchen flows and feet washing flows in all likelihood will <br /> cancel each other out with respect to organic loading. Blackwater will originate from toilets and <br /> will be a smaller volume than the kitchen and feet wash wastewater flow volumes. Additional <br /> wastewater constituents may consist of other liquids to the system, such as juices, etc. No industrial <br /> or commercial chemicals, solvents, etc. should be introduced into the septic treatment system. <br /> The scientific literature (Ref. 9) cites nitrogen concentrations in septic effluent typically ranging <br /> from 17 mg N/L for basins, sinks, etc. to 140 mg N/L for toilet wastes. Therefore, considering a <br /> 70/30 percent usage for toilet blackwater nitroge5cp1trations and feet wash/kitchen graywater <br /> nitrogen concentration, respectively, a valu of 1L of is effluent will be used to <br /> calculate nitrate-nitrogen loading for this pr of 62 mg is typically used for <br /> residential calculations, as indicated in the scientific liter e , Pg.149). <br /> This value of 103 mg/L is extremely conservative given that domestic household blackwater wastes <br /> (toilet), graywater wastes(showers, laundry, tooth brushing), and kitchen wastes (food, cooking <br /> oils, dishwashing) would be expected to be a much higher(an estimate being three to four times <br /> higher) nitrogen concentration than what is projected from the Hindu Cultural Center. <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. Loading projections are normally based on the maximum <br /> anticipated wastewater flows. The numbers of on-site Parishioners has been defined by Mr. Iyer for <br /> the project and has been specified in the Use Permit Application for a Use Permit. <br /> The San Joaquin County Onsite Wastewater Disposal Standards assigns 10 gallons per seat(person) <br /> when there is a kitchen in a House of Worship. Therefore, considering the total n ed le <br /> on a weekly basis, we have: 81 people x 10 gals/person x 1 d/week on Saturday = 810 gals <br /> Total wastewater flow per week= 810 gals/wk <br /> Total wastewater flow per year= 810 gals/wk x 52 weeks/yr—42,120 gals/yr <br /> 8 <br />
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