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SU0003927 SSNL
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SU0003927 SSNL
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Last modified
5/7/2020 11:30:20 AM
Creation date
9/9/2019 9:02:50 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0003927
PE
2622
FACILITY_NAME
PA-0200271
STREET_NUMBER
651
Direction
S
STREET_NAME
REID
STREET_TYPE
AVE
City
LINDEN
ENTERED_DATE
5/11/2004 12:00:00 AM
SITE_LOCATION
651 S REID AVE
RECEIVED_DATE
7/11/2002 12:00:00 AM
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\R\REID\651\PA-0200271\SU0003927\SS STDY.PDF
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EHD - Public
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KLEINFEL DER <br /> On October 14, 2002, a staff geologist with our firm obtained a sample of groundwater using <br /> clean procedures from a spigot on a residential home located northea That same <br /> day, the water sample was submitted to equoia Analytical using chain-of-custody procedures <br /> for DBCP and nitrate testing. The results of these tests and a copy of the chain-of-custody are <br /> attached to this letter. <br /> NITRATE LOADING CALCULATIONS <br /> Per SJCEHD requirements, the following summarizes our nitrate loading calculations for the <br /> proposed leach fields. The drinking water standard for nitrate is 45 milligrams per liter (NOO <br /> and 10 mg/1 as Nitrogen (1) in groundwater. In our evaluation of nitrate loading, we have used <br /> the Hantzsche mass balance equation (source: Predicting Ground-Water Nitrate-Nitrogen <br /> Impacts, Hantzsche and Finnemore (1992)), which is presented below with an explanation for <br /> each factor and the value used in our study. Since there is currently no deed restriction limiting <br /> the number of homes on each lot to one, we have calculated the average nitrate (Ne) in <br /> groundwater based on two homes per lot as required by Mr. Huggins with SJCEHD. The <br /> selection of other parameters was based on previous studies by our firm, a report dated March <br /> 19, 1997 prepared by the Questa Engineering Corporation and authored by Mr. Hantzsche for a <br /> development in the Stockton area, and communications with Mr. Huggins. <br /> Ne =AWNw (1-D)+(Nb)r <br /> AW+r <br /> Where: <br /> Ne = Average calculated nitrate in groundwater resulting from domestic sources and <br /> precipitation—mg/l, as N <br /> A = Number of dwelling units per acres on septic tanks (unit/acre) = 1.00 (estimated <br /> based on 8 homes divided by 8 acres) <br /> W = Annual wastewater loading per dwelling unit per acre (inches) = 2.0 inches (based on <br /> 150 gpd/residence) <br /> Nw = Nitrate concentration of nitrified leachfield effluent (mg/1) = 35 mg/l typical (per <br /> Mike Huggins) <br /> D = Percent denitrification of leachfield effluent = 0.25 percent (0.1 to 0.35 percent <br /> typical per Hantzsche and Finnemore (1992). 0.25 selected given the large depth to <br /> groundwater and the presence of interbedded low permeable clay layers.) <br /> r = Annual deep percolation of precipitation (inches) = 9.8 inches (representing 70 <br /> percent of the average annual rainfall of 14 inches in project area. Remaining 30 <br /> percent of rainfall is assumed to drain off-site into natural or manmade drainages) <br /> Nb = Background nitrate concentration of the deep percolating precipitation — mg/1 = 0.5 <br /> mg/l (per Technical Memorandum, Hydrologic and Soil Investigation for the Chico <br /> Urban Area,page 6, Dames and Moore, April 1996) <br /> 23197.G01/ST03R290 February 14,2003 <br /> ©2003 Kleinfelder,Inc. Page 3 of 4 <br />
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