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SU0005295_SSNL
Environmental Health - Public
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SU0005295_SSNL
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Last modified
11/19/2024 1:52:16 PM
Creation date
9/8/2019 12:49:13 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0005295
PE
2611
FACILITY_NAME
SU-91-12
STREET_NUMBER
10600
Direction
N
STREET_NAME
STATE ROUTE 99
City
LODI
APN
08607035
ENTERED_DATE
8/15/2005 12:00:00 AM
SITE_LOCATION
10600 N HWY 99
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\sballwahn
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FilePath
\MIGRATIONS\N\HWY 99\10600\SU-91-12\SU0005295\NL STDY.PDF
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EHD - Public
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I <br /> KLEINFELDER <br /> upper acquifer. In discussions with the Environmental Health Division (EHD), we understand <br /> that similar observations have been made by San Joaquin County. Nevertheless, in order to be <br /> consistent with requirements for the adjacent subdivisions in the area, and because of the <br /> calculated nitrate loading value, we understand that some enhanced features of the leach field <br /> design will be required by San Joaquin County. Although the final system design for this project <br /> was provided by Valley Ag Research and is presented below, we recommend that all seepage <br /> pits extend at least 20 feet in depth, because of the variability of the more permeable sand lenses <br /> on which our percolation tests were generally performed. <br /> SYSTEM DESIGN <br /> The system design prepared by Don Chesney of Valley Ag Research is presented on Plate 1 <br /> attached and is described below. As stated, all details of the system must comply with the San <br /> Joaquin County Environmental Health Division Sewage Standards (11/96). We suggest that new <br /> home owners sign Plate 1 acknowledging receipt and acceptance of the construction and <br /> maintenance procedures. As you are aware our analysis indicates a nitrate loading above the <br /> maximum level of 10 mg/L. According to Mr. Chesney, nitrate-nitrogen impact mitigation will <br /> be primarily accomplished by using two septic tanks through the following processes: It has <br /> been well documented that gaseous nitrogen emanates from septic tanks. The gaseous formation <br /> is apparently attributable to denitrification which is the biological reduction of nitrate (NO3) and <br /> nitrate (NO2) to volatile gases. The biochemical processes that occur in septic tanks are highly <br /> complex, but can be described simplistically: A microbe digesting a waste organic molecule <br /> with an attached nitrogen atom may have the freed nitrogen as a surplus atom. To digest the N <br /> atom, the microbe can combine it with dissolved molecular oxygen 02 and release it in solution <br /> as a molecule of nitrite or possibly nitrate. This occurs under aerobic conditions and is referred <br /> to as nitrification. If a microbe needs oxygen within an anaerobic environment, it can take the <br /> oxygen from nitrite or nitrate molecules. Not requiring surplus nitrogen atoms, the microbe can <br /> combine pairs of surplus nitrogen atoms to form nitrogen gas (N2). This is called denitrification. <br /> Therefore, by using two septic tanks in series, the first tank should contain some oxygen from <br /> sink faucet aeration and the flushing action of toilets. This should promote nitrification. As the <br /> oxygen is consumed in the first tank, effluent flowing into the second tank should be <br /> predominately anaerobic, if this tank is sealed. Under these conditions, denitrification should be <br /> promoted in the second tank. <br /> The following data was obtained from J.H.T. Winneberger, Sotic-Tank Systems — A <br /> Consultant's Toolkit which substantiates the process of denitrification within septic tanks: <br /> Argon is an inert gas found in the atmosphere in proportions of 84 parts of nitrogen to one part <br /> argon. When each of these gases come to equilibrium in water under one atmosphere of <br /> pressure, they exist in a ration of approximately 37 parts of nitrogen to one part argon. <br /> Analytical data obtained from septic tank effluent should also correlate with this ratio unless <br /> gaseous nitrogen (N2) is liberated. Calculations of nitrogen:argon ratios obtained from the <br /> analyses of seven different effluents indicate ratios of 100, 60, 43, 50, 60, 54 and 41. All these <br /> values exceed the expected nitrogen:argon ration of 37 and suggest nitrogen gas liberation. This <br /> data supports the theory that denitrification occurs within septic tanks and by using two tanks in <br /> series, theoretically encourages the denitrification process. <br /> Other details of the Double System Design are shown on Plate 1. Please note that the number <br /> and length of leach lines shown is for a single leach field and must be doubled per county <br /> standards. In addition all set back and dimensional requirements shown on Plate 1 and described <br /> in Sewage Standards must be followed by the civil engineer or architect on the project. <br /> 20-2921-02/2011 R1169 Page 4 of 5 <br /> Copyright 2001 Kleinfelder,Loc. September 25,2001 <br />
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