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SU0000021 SSNL
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MS-01-14
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SU0000021 SSNL
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Last modified
5/7/2020 11:27:33 AM
Creation date
9/6/2019 10:13:55 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0000021
PE
2622
FACILITY_NAME
MS-01-14
STREET_NUMBER
15444
Direction
S
STREET_NAME
MITCHELL
STREET_TYPE
RD
ENTERED_DATE
8/8/2001 12:00:00 AM
SITE_LOCATION
15444 S MITCHELL RD
RECEIVED_DATE
4/13/2001 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\M\MITCHELL\15444\MS-01-14\SU0000021\NL STDY.PDF
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EHD - Public
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The concentration of nitrogen in septic system effluent is normally specified as units of mg NIL. <br /> Unfortunately,these units superimpose wastewater flow variability onto nitrogen influent `~ <br /> variability,thus creating even greater variability. The above figure for wastewater discharge is <br /> estimated at iMals/resident/day (428 Liters , and using the figure of 17 g N/cap/day excreted <br /> 17 g-428 L =40 mg N/L/day. This nitrate-nitrogen concentration will be the estimated <br /> nitrogen loading in the effluent discharged from the two proposed SFRs. <br /> D. CALCULATED IMPACT FROM NITRATE-NITROGEN LOADING <br /> The calculated or estimated nitrate impact to the soil originating from septic effluent, and <br /> ultimately impacting the groundwater is extremely difficult to determine due to the number of <br /> variables involved. With this project, only the two proposed new homesite Parcels will be taken <br /> into consideration and not the total area, which includes the existing homesite on the Designated <br /> Remainder. This will be done so that a comparison can be made between nitrate loading from <br /> the existing almond orchard on proposed Parcels I and 2, and nitrate loading from two new <br /> homesites on these same Parcels. It is assumed that a traditional septic system will be installed <br /> for each residential structure. Therefore, the following calculations are based upon using a <br /> conventional or traditional type of a septic system consisting of a septic tank, leachfield and <br /> possibly filter beds or sumps. <br /> HANTZSCHEIFINNEMORE EQUATION <br /> M,(1 - d) +RN <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 <br /> inches per yr <br /> Nw= Total nitrogen concentration of wastewater in N mg/L (40 mg NIL/day) <br /> d = Fraction(%) of nitrate-nitrogen loss due to denitrification in the soil <br /> R = Average recharge rate of rainfall - inches per yr (11) <br /> Nb = Background nitrate-nitrogen concentration of rainfall recharge, exclusive of wastewater <br /> influences (0.1 ppm NO3-N) <br /> Values and Assumptions <br /> 113 gals/person/day x 4 people per household x 2 new houses/4.5 Ac x 365 d/yr =2.7 in. <br /> I = 43,560 cu ft/Ac ft x 7.48 gal/cu ft x (I.ft/12 in) <br /> Nw=40 mg/L - 20% reduction from typ. septic tank = 32 mglL N <br /> d — 10% from biomat and 15%from saturated soil conditions under leachlines. <br /> Nb = Assumed to be 0.1 ppm NO3-N <br /> 8 <br /> Vafley dig Research <br />
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