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SU0007284 SSNL
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SU0007284 SSNL
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Last modified
5/7/2020 11:32:58 AM
Creation date
9/9/2019 9:06:05 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0007284
PE
2631
FACILITY_NAME
PA-0800197
STREET_NUMBER
25192
Direction
E
STREET_NAME
RIVER
STREET_TYPE
RD
City
ESCALON
APN
247-090-40
ENTERED_DATE
7/14/2008 12:00:00 AM
SITE_LOCATION
25192 E RIVER RD
RECEIVED_DATE
7/14/2008 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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FilePath
\MIGRATIONS\R\RIVER\25192\PA-0800197\SU0007284\NL STDY.PDF
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EHD - Public
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Soil Suitability& Nitrate Loading Study <br /> Munoz Property, Escalon, CA Page 9 <br /> Project No. 605.1 <br /> June 18, 2009 <br /> ` 7.0 NITRATE LOADING <br /> T I ximum allowable nitrate as nitrogen concentration in drinking water is <br /> 0' m /L. The introduction of human or animal wastes to the soil introduces <br /> itr e and nitrate-forming compounds, which can be leached downward, enter <br /> the groundwater and possibly degrade drinking water- These concerns triggered <br /> a requirement by the EHD that an estimate be made of the amount of nitrate <br /> that could reach groundwater as a result of construction of the proposed septic <br /> system. <br /> In 1992, Hantzsche and Finnemore published a simple mass-balance method of <br /> ri <br /> estimating the amount of nitrate that can be expected to reach groundwater <br /> from a septic system, and this model has become commonly accepted as a "first- <br /> look" approach. The model takes into consideration the volume and nitrate <br /> concentration of the effluent, the de-nitrification effect of the soil, and the <br /> amount and annual rainfall. The original paper stipulated, however, that while <br /> the model is useful for planning purposes, it suffers from limitations. The <br /> ` limitation is due to the introduction of simplifying assumptions; especially in <br /> neglecting the effects of dispersion and diffusion in groundwater flow. The <br /> model estimates the long-term concentration of nitrate in the upper-most <br /> groundwater layer, but ignores the effect that the mixing with deeper <br /> groundwater will have on overall nitrate concentration. These assumptions will <br /> generally tend to result in an over-estimation of nitrate loading. The Hantzsche- <br /> Finnemore model is a conservative tool, useful as a "first approximation" for <br /> long-term effects of nitrate sources, but it may not accurately reflect actual <br /> groundwater conditions closely. <br /> The actual Hantzsche-Fmnemore equation is shown on the calculation sheets in <br /> Appendix E. <br /> 7.1 . Input Data to the Model <br /> The following points summarize key factors input to the nitrate loading model: <br /> FjNitrate in Efflicent <br /> According to Rosen et. al., (2006), the , itra e ncentration of septic tank <br /> effluent is variable, but the average is ab ut 44 mg/L. <br /> Meteoric Water <br /> Rainwater percolating through the soil is the primary leaching agent carrying <br /> nitrates to the groundwater. The estimate of the amount of deep percolation is <br /> based, in part of the long-term average annual precipitation and on the average <br /> 2937 Veneman Ave.,#$240 Geo-Phase Environmental Inc. Phone: (209) 569-0293 <br /> Modesto, CA 95356 Fax: (209)569-0295 <br /> f <br /> I <br /> M <br />
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