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SU0004529 SSNL
Environmental Health - Public
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SU0004529 SSNL
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Last modified
5/7/2020 11:30:52 AM
Creation date
9/5/2019 10:48:01 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0004529
PE
2689
FACILITY_NAME
PA-0400351
STREET_NUMBER
3703
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
953049515
APN
21327013 & 14
ENTERED_DATE
7/6/2004 12:00:00 AM
SITE_LOCATION
3703 W GRANT LINE RD
RECEIVED_DATE
6/30/2004 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\G\GRANT LINE\3703\PA-0400351\SU0004529\NL STDY.PDF
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EHD - Public
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rTr�B7. CALCULATED <br /> NITRATE-NITROGEN LOADING <br /> The calculated nitrate-nitrogen impact to the soil and ultimately to the groundwater is difficult to <br /> determine due to the large number of variables involved, and variables unknown at this time. These <br /> variables include: 1.) Future installation methods and design of the on-site septic system for a future <br /> project, 2.)Impact from upgradient nitrate sources, 3.)Variability in wastewater flows, nitrogen <br /> concentrations and dilution effects from effluent and stormwater recharge, 4.) Changes in <br /> groundwater directional flow and elevation, 5.)Denitrification potential within the soil environment <br /> and within the confined and unconfined aquifers and 6.) Potential landscape uptake of nitrogen. <br /> Various scientific methods exist to estimate nitrate-nitrogen loading. This study uses the <br /> k Hantzsche/Finnemore Formula to predict the average resultant concentration of nitrate-nitrogen in <br /> effluent recharge water. As calculated below, the property has been assessed on a total areal loading <br /> basis correlated with the total number ofpeople on-site everyday of the year. These two factors <br /> primarily dictate the average resultant concentration of nitrate-nitrogen in the recharge water, which <br /> cannot exceed 10 ppm nitrate-nitrogen (45 ppm as nitrate). As referenced, the current water table <br /> nitrate concentration has been measured at 71 ppm N031 which should be considered the baseline. <br /> Depending upon the interpretation of the Porter-Cologne Water Act, it is assumed that the nitrate <br /> concentration of the resultant septic system effluent e cannot exceed this current water table <br /> concentration of 71 ppm NO3. The following Calc a i ns d onstrate t esul t effluent recharge <br /> water from a proposed future project will not exce d 10 ppm NO3-N, o 45 ppm 03. This is a 37% = <br /> reduction in nitrate concentration between the recti gc effl t and the a 'sting w ter table nitrate <br /> concentration. <br /> PREDICTED NITRATE- TROGEN LOADING OM A COMPLETELY BUILT- <br /> OUT PROJECT USIN AN E.H.D. APPROVED S PTIC SYSTEM. THE MAXIMUM <br /> NUMBER OF PEOPLE PN 213-270-14 1.03 Acres AN SUPPORT WITHOUT <br /> EXCEEDING THE M.C.L. OR NITRATE (10 PP NO3-N) = <br /> HA NTZS CHEIFINNEMORE EQUATION <br /> f <br /> +R Nb <br /> Nr= (I+ R) <br /> Values and Assumptions: <br /> I=7 eo Ie Maximum x 15 als/ erson/d x 365 d/ r=38 325 als=total WWI =5 124 cu ft= 1.38 in/yr <br /> 1.03 Ac x 43,560 sq ftlAc x (1 fU12 in) <br /> Nw= 103 mg NIL <br /> d = Assume 20% due to fine-grained soil <br /> R = 10 in/yr. <br /> Nb= Assumed to be 0.1 ppm NO3-N <br /> 11 <br /> Chesney Consulting <br />
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