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SU0002680 SSNL
Environmental Health - Public
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SU0002680 SSNL
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Last modified
5/7/2020 11:29:24 AM
Creation date
9/6/2019 11:02:01 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002680
PE
2633
FACILITY_NAME
SA-99-52
STREET_NUMBER
25650
Direction
E
STREET_NAME
LONE TREE
STREET_TYPE
RD
City
ESCALON
APN
22908074
ENTERED_DATE
10/31/2001 12:00:00 AM
SITE_LOCATION
25650 E LONE TREE RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\L\LONE TREE\25650\SA-99-52\SU0002680\NL STDY.PDF
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EHD - Public
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"— In KL EINEELDER <br /> the Hantzsche mass balance equation (source: Predicting Ground-Water Nitrate-Nitrogen <br /> Impacts, Hantzsche and Finnemore (1992)), which is presented below with an explanation for <br /> each factor and the value used in our study. The selection of parameters was based on previous <br /> studies and investigations performed by our firm and others, San Joaquin County Sewage <br /> Standards, and information provided in a report dated March 19, 1997 prepared by the Questa <br /> Engineering Corporation and authored by Mr. Hantzsche for a development in the Stockton area. <br /> Ne=AWNw 1-D + bZr <br /> AW+r <br /> Where: <br /> Ne = Average calculated nitrate-nitrogen in groundwater resulting from domestic sources <br /> and precipitation—mg/l, as N <br /> A = Number of dwelling units per acre on septic tanks (unit/acre) = 0.89 (estimated <br /> based on an estimated water usage of 150 gal./day (see below) which is equivalent <br /> to the typical daily water usage for 3 bedroom residential home) <br /> W = Annual wastewater loading per dwelling unit per acre (inches) = 1.27 inches (based <br /> on 5 workers with a water usage of 30 gal./shift (San Joaquin County Sewage <br /> Standards for day workers at offices) assuming 5 work days/week) <br /> Nw = Nitrate concentration of nitrified leachfield effluent (mg/1) = 35 mg/1 typical <br /> (Hantzsche and Finnemore (1992)) <br /> D = Percent dentrification of leachfield effluent = 0.35 percent (0.1 to 0.35 percent <br /> typical per Hantzsche and Finnemore (1992). 0.35 selected given the large depth to <br /> groundwater (>75 feet) and a majority of the soils encountered consist of fine clays <br /> and silts that tend to increase denitrification) <br /> R = Annual deep percolation of precipitation (inches) = 6.0 inches (representing 50 <br /> percent of average annual rainfall in project area. Remaining 50 percent of rainfall <br /> is assumed to fall on on-site improvements and/or drain off-site into natural or <br /> manmade drainages) <br /> Nb = Background nitrate concentration of the deep percolating precipitation — mg/I = 2.2 <br /> mg/l as N <br /> Our calculation is as follows: <br /> Ne = 0.89(1.27)(35)(1 —0.35) +2.2(6) = 25.7 + 13.2 = 5.45 mg/1 as N <br /> .89(1.27)+6 1.13 +6 <br /> CONCLUSIONS <br /> Based on the above evaluation, we conclude that wastewater produced by the proposed office <br /> building should not cause the nitrate levels in groundwater below the site to rise above the state <br /> 204585-0LG01/2011 R602 November 21,2001 <br /> ©2001 Kleinfelder,Inc. Page 3 of 4 <br />
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