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SU0009972 SSNL
Environmental Health - Public
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SU0009972 SSNL
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Last modified
5/7/2020 11:34:19 AM
Creation date
9/5/2019 11:19:53 AM
Metadata
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EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0009972
PE
2631
FACILITY_NAME
PA-1400042
STREET_NUMBER
9851
Direction
E
STREET_NAME
HUTCHINSON
STREET_TYPE
RD
City
MANTECA
Zip
95336-
APN
25724048
ENTERED_DATE
3/4/2014 12:00:00 AM
SITE_LOCATION
9851 E HUTCHINSON RD
RECEIVED_DATE
3/3/2014 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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\MIGRATIONS\H\HUTCHINSON\9851\PA-1400042\SU0009972\NL STDY.PDF
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EHD - Public
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effluent recharge water. As calculated below, the property has been assessed on a total areal loading <br /> basis of 7 acres representing the Project Size, correlated with the 300 gallons total per_dayfrom both <br /> restrooms, as noted above, with each toilet at 150 gals/day per EHD Standards. 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). Additionally, as a highly significant <br /> safety factor,wastewater flows are based on every day of the year and not on the relatively short <br /> operational duration of a few months as indicated on the Site Approval Application. The following <br /> calculations demonstrate the resultant effluent recharge water from the project will be substantially <br /> below pm NO3-N, or 45 ppm NO3- <br /> /NLS§3.4,3.5,3.6 ,PREDICTED NITRATE-NITROGEN LOADING FROM THE PROPOSED COMPLETE <br /> BUILD-OUT RIVER OAK ORCHARD WALNUT PACKAGING FACILITY AND THE <br /> PRECISIO HULLING FACILITY: <br /> HANTZSCHEIFINNEMORE EQUATION <br /> IN�(1 - d)+RNb <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 loss due to denitrification in the soil <br /> R = Average recharge rate of rainfall - inches per yr NLS§3.2 <br /> Nb= Background nitrate-nitrogen concentration of rainfall recharge,exclusive of wastewater influences <br /> (ppm NO3-N) <br /> Values and Assumptions <br /> I= 300 2od t 365 d/ ,r= 109,500 gals=total WW/yr= 14,639 cu ft = 0.58 in. <br /> 7 Ac x 43,560 sq ft/Ac x(1 ft/l2 in.) <br /> Nw = 103 mg N/L 20%reduction from the septic tank =(1-0.2)103 = 82 mg N/L <br /> d = Assume 20%due to the fine-grained soil at the potential soil-effluent interface soil chemistry results. <br /> R = 12 in/yr. <br /> Nb= Assumed to be 0.1 ppm NO3-N <br /> 0.58 in/yr(82 mg,N/L)(1 -0,20).+(12 in/yr x 0.1 nw,/L) <br /> Nr (0.58 in/yr+ 12 in/yr) <br /> Nr — 3.1 :e-d <br /> m as ' rate-nitrogen(NO3-N)or 14.0 ppm as nitrate(NO3) <br /> The ca nitrate loading concentration in the recharge effluent from the Men's and Women's <br /> Restroom is calculated to be under the Maximum Contaminant Level limit for nitrate in drinking <br /> water, and is equal to the existing nitrate concentration in the on-site well water. The variables <br /> used in the calculations above are conservative. For example, the use of 103 mg N/L, is a much <br /> higher nitrogen concentration than those concentrations published from household or domestic <br /> sources. From the May 8, 2003 Symposium"Onsite Wastewater Treatment-Nitrogen Removal," <br /> 8 <br />
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