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SU0001237 SSNL
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SU0001237 SSNL
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Last modified
5/7/2020 11:28:33 AM
Creation date
9/8/2019 1:04:12 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0001237
PE
2690
FACILITY_NAME
LA-00-57
STREET_NUMBER
18404
Direction
S
STREET_NAME
NORTH RIPON
STREET_TYPE
RD
City
RIPON
APN
24504003
ENTERED_DATE
10/18/2001 12:00:00 AM
SITE_LOCATION
18404 S NORTH RIPON RD
RECEIVED_DATE
7/24/2000 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\N\NORTH RIPON\18404\LA-00-57\SU0001237\NL STDY.PDF
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EHD - Public
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The characteristics or composition of septic tank effluent is dependent upon several parameters <br /> because of idiosyncrasies within each household. Certain appurtenances change the <br /> characteristics of the wastewater effluent such as filter vaults within septic tanks and kitchen <br /> food-waste grinders. Since this study is concerned with nitrogen,this constituent is quantified in <br /> the effluent,below: <br /> In determining nitrogen concentrations of septic influent and effluent, per capita intake of <br /> nitrogen per day must be estimated. The average American consumes between 70 and 140 g of <br /> N/day. Since nitrogen comprises 16%of the weight of the average protein, 16%of 70 g N= 11 <br /> g N/capita/day and 16%of 140 g N=22 g N/capita/day. The average of these two values is 17 g <br /> N/capita/day of theoretical influent. <br /> The concentration of nitrogen in septic system effluent is normally specified in the scientific <br /> literature as units of mg N/L. Unfortunately, these units superimpose wastewater flow variability <br /> _ onto nitrogen influent variability, thus creating even greater variability. One researcher, <br /> (Bauman),has averaged the means from 20 other studies to arrive at a concentration of 62 f 21 <br /> mg N/L in septic tank effluent. If the above figure for wastewater discharge is estimated at 68 <br /> _ gals/resident/day (257 liters)and using the figure of 17 g N/cap/day excreted= 17 g=257 L=66 <br /> mg N/L/day estimated for the proposed project. This concentration will be the estimated <br /> nitrogen loading in the effluent discharged throughout the project. <br /> D. CALCULATED IMPACT FROM NITRATE-NITROGEN LOADING <br /> The calculated or estimated nitrate impact to the soil and ultimately to the groundwater is <br /> extremely difficult to determine due to the number of variables involved. With this project, only <br /> the area of the proposed new eight homesite Parcels will be taken into consideration and not the <br /> total area of all 11 Parcels. Therefore, only the nitrate loading from the new development will be <br /> quantified and compared with 1.) leaving this acreage in agricultural production and 2.)with the <br /> current nitrate concentration in the groundwater. It is assumed that a traditional septic system <br /> will be installed for each residential unit. Consequently,the following calculations are based on <br /> using a conventional or traditional type of a septic system consisting of a septic tank and <br /> leachfield. Three different nitrate loading methods are presented, as described by each respective <br /> author/researcher: <br /> HANTZSCHEIFINNEMORE EQUATION <br /> al,(I - d) +RNb <br /> Nr= (I + R) <br /> Where: <br /> L 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 (66 mg N/L/day) <br /> 8 �Ji <br /> LNa!(ey lig Research <br />
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