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SU0002535 SSNL
Environmental Health - Public
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SU0002535 SSNL
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Entry Properties
Last modified
5/7/2020 11:29:17 AM
Creation date
9/4/2019 6:42:15 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002535
PE
2633
FACILITY_NAME
SA-00-74
STREET_NUMBER
301
Direction
E
STREET_NAME
FRENCH CAMP
STREET_TYPE
RD
City
FRENCH CAMP
APN
19313031
ENTERED_DATE
10/29/2001 12:00:00 AM
SITE_LOCATION
301 E FRENCH CAMP RD
QC Status
Approved
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SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\F\FRENCH CAMP\301\SA-00-74\SU0002535\NL STDY.PDF
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EHD - Public
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... ."we <br /> F <br /> RATE LOADING STUDY FINDINGS <br /> STEWATER FLOW CALCULATIONS AND CHARACTERISTICS <br /> oaequately determine nitrogen loading from the Church, wastewater flows must be <br /> determined as accurately as possible. As with most Churches, Sunday is the heaviest wastewater <br /> flow day of the week, which influences flow estimates and design criteria. The following <br /> calculations illustrate flow projections: <br /> With the new building addition,there will be a c=acitof 210 Parishioners. According to Mr. <br /> Rodgers there is approximately 180 members of the Church, with an average Sunday attendance <br /> of approximately 150. Additional meetings include a small weekly meeting every Tuesday of 5 <br /> people and a monthly Council Meeting consisting of approximately 15 people (average <br /> people/wk). ac or, spe ' events such as bazbeques, car washes, etc. may <br /> the a 17 people per we k For example: 6 major events throughout the year with 150 - <br /> people at each ev = 6 events N50 people/event - 5weeks/yr= 17 people/wk. Therefore /J� <br /> the flow projections are as follows: <br /> ��s��orSS�'�'c'F <br /> r--(� �1�6 5 +4 people/wk x 5 gals/person=�fisU gals/wk=7 days/wk <br /> `IS&Zals/day=Average Daily Flow(ADF) <br /> It is our understanding that there is no kitchen for food preparation,thus reducing the organic <br /> loading that would normally be found in a Church kitchen having a garbage grinder or disposal. <br /> The characteristics of the wastewater flow will be predominately blackwater, with a <br /> comparatively small volume of sink water and no graywater from the washing of clothes, <br /> bathing, etc. <br /> B. CALCULATED IMPACT FROM NITRATE-NITROGEN LOADING <br /> From the anticipated wastewater characteristics described, the nitrogen originating from the <br /> Church may be at a higher concentration than what would normally be found in a typical <br /> domestic or household system. This can be attributed to the lack of a dilution effect which <br /> graywater would provide. In contrast, it can be theorized the nitrogen concentration may be less <br /> because anticipated toilet habits may differ from a residential setting. <br /> Data found in Table 4-16 of Small and Decentralized Wastewater Management Systems <br /> indicates the Total Kjeldahl Nitrogen(TKN)concentration in the effluent from a residential <br /> septic tank with an effluent filter vault ranges between 50 and 90 mg TKN/L. For conservative <br /> purposes, the highest value of 90 ppm TKN will be used in the following calculations. The TKN <br /> fraction is the total of the organic and ammonia-nitrogen fractions of nitrogen and it is <br /> conservatively assumed that this nitrogen concentration has the pential to all be oxidized, or <br /> converted to nitrate. The areal contribution of nitrate in terms of pounds per acre is as follows: <br /> 126 gals/day (ADF)x 3.79 L/gal =478 L/day x 90 mg N/L= 43 grams N/day x 365 days/yr T) <br /> 16 kg N/yr x 2.2 Ib/kg= 35 lbs N/yr_ 0.92 Ac= 37 lbs N/Ac/yr(Total areal contribution). <br /> Page-4- <br /> VaCley Ag Research <br />
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