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SU0005897 SSNL
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SU0005897 SSNL
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Last modified
5/7/2020 11:31:51 AM
Creation date
9/6/2019 10:03:52 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0005897
PE
2691
FACILITY_NAME
PA-0600037
STREET_NUMBER
11293
Direction
S
STREET_NAME
MANTHEY
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19125008
ENTERED_DATE
1/31/2006 12:00:00 AM
SITE_LOCATION
11293 S MANTHEY RD
RECEIVED_DATE
1/31/2006 12:00:00 AM
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\M\MANTHEY\11293\PA-0600037\SU0005897\NL STDY.PDF
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EHD - Public
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i <br /> Resultant Recharge(Nr)from the Gas Station and Convenience Store exclusively is at the Maximum <br /> Contaminant Level(MCL)for nitrate-nitrogen of 10 ppm. <br /> 5.3 Crites / Tchobanoglous Formula (Phase 1 & Complete Build-Out) <br /> LN = Lµ,CNF <br /> where: <br /> LN = nitrate-nitrogen loading in lbs/ac-day <br /> LW = wastewater loading in gals/ac-day= 25,830 gals/day= 11 ac=2,350 gals/ac-day <br /> CN = nitrogen concentration: average determined to be 87 mg N/L <br /> F = conversion factor: 8.34 lbs/[106 gal-(mg/L)] <br /> LN= 2,350 gals/ac-day x 87 mg N/L x (8.34)(10-6) = 1.71 lbs N/ac•day x 365 days/yr= <br /> 622.4 lbs N/ac/yr. The disposal area could be a maximum of 3.1 acres. Therefore,the <br /> Crites/Tchobanoglous Formula nitrate-nitrogen loading is approximately 622.4 lbs N/ac/yr <br /> x 3.0 acre =1,870 lbs N/yr. <br /> Comparing the Hantzsche/Finnemore Equation with the Crites/Tchobanoglous Formula by <br /> using the results from the Hantzsche/Finnemore Equation of 50.5 ppm NO3 N (223.6 ppm NO3): <br /> 50.5 ppm nitrate-nitrogen x 2.72 (conversion factor) = 137.4 lbs N in an acre-foot of water. <br /> 9,428,000 gallons wastewater/yr '. 325,851 gals/ac-ft water=28.9 ac-ft of wastewater disposed/yr <br /> x 137.4 lbs N/ac-ft= 3,975 lbs N/yr according to the Hantzsche/Finnemore Equation. Therefore, <br /> the Crites/ Tchobanoglous Formula predicts approximately 2.1 times less (approx. one-half) <br /> nitrate-nitrogen loading (in terms of lbs N/yr) than predicted by the Hantzsche/Finnemore <br /> Equation (1,870 lbs N/yr vs. 3,975 lbs N/yr). <br />! 5.4 Kaplan Parallelepiped Method (Phase 1 & Complete Build-Out) <br /> NLS§3.6 <br /> Assumptions: 1.) The entire concentration of Total Nitrogen (87 ppm) is completely nitrified and <br /> percolates to the water table, 2.) Water table depth of 22 ft, and a 15 ft mixing layer thickness of <br /> the first aquifer, 3.) Porosity is 33%, 4.) The entire length(N-S) of the disposal area is used (250 <br /> ft), 5.)No nitrogen input from on-site landscape fertilization or indigenous soil nitrogen, 6.) <br /> Water table Darcy velocity has been calculated on Pg. 12 to be 1.0 ft/day, 7.) Groundwater flow <br /> direction is due north. <br /> Volume of dilution: <br /> 250 ft length x 15 ft depth mixing layer x 1 foot/day x 365 days/yr x 1 m'/35.3 ft' = 38,775 <br /> m'/yr=38,775,000 kg water/yr x 33%porosity= 12,796,000 kg water/yr. <br /> Amount of Nitrate: <br /> Taking the average of the lbs N/yr as determined from the Hantzsche/Finnemore Equation= <br /> 3,975 lbs N/yr x 0.4536 (conversion factor) = 1,803.1 kg N/yr <br /> Increase in Mixing Laver Concentration: <br /> 1,803.1 kg N_ 12.796 million kg water= 140.9 ppm NO3-N (624.0 ppm NO3). <br /> The increase in mixing layer nitrate concentration as predicted by the Kaplan Method is 2.8 times <br /> greater than the Hantzsche/Finnemore Equation determination (140.9 ppm N0;N vs. 50.5 ppm <br /> NO3-N)' <br /> Page -21- <br /> Chesney Consulting <br />
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