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SU0007346 SSNL
Environmental Health - Public
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SU0007346 SSNL
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Entry Properties
Last modified
5/7/2020 11:33:00 AM
Creation date
9/6/2019 10:08:08 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0007346
PE
2631
FACILITY_NAME
PA-0800247
STREET_NUMBER
33
Direction
W
STREET_NAME
MATHEWS
STREET_TYPE
RD
City
FRENCH CAMP
APN
19316026
ENTERED_DATE
8/25/2008 12:00:00 AM
SITE_LOCATION
33 W MATHEWS RD
RECEIVED_DATE
8/22/2008 12:00:00 AM
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\M\MATHEWS\33\PA-0800247\SU0007346\NL STDY.PDF
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EHD - Public
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Bail Bond Business Page 8 of 13 <br /> Our Project Number: LGS080549 <br /> January 13, 2009 <br /> The method utilized for the nitrate loading analysis is based on a simple mass balance formula, <br /> discussed in a published article by Hantzsche and Finnemore (1992), which provides a <br /> convenient and simplified method to estimate long-term ground-water nitrate impacts on an <br /> area-wide basis. <br /> Hantzsche and Finnemore found that over a long period of time, water quality in the upper <br /> saturated ground-water zone closely approximates the quality of percolating recharge waters. <br /> They believe that their method is a good planning tool and provides useful information to <br /> planners and local officials but with some real limitations. In their article published in Ground <br /> Water, Hantzsche and Finnemore mention that "...the equation ignores dispersion, lateral flow, <br /> and mixing with ground water flow from up-gradient areas. These processes would generally <br /> contribute to additional reduction of nitrate-nitrogen concentrations in ground water to the <br /> extent that the nitrate-nitrogen concentration of ground-water flow from up-gradient areas is <br /> lower." <br /> The Hantzsche and Fennemore approach is "...a conservative (worst case) first approximation <br /> of ground-water nitrate-nitrogen concentration resulting from the combined effect of on-site <br /> sewage disposal systems and precipitation. This (the equation and approach) is for estimation <br /> of long-term effect (i.e., over years) on ground-water quality, and is not intended for prediction <br /> of seasonal changes" (Hantzsche and Finnemore, 1992). <br /> The method takes into account the development area, soil denitrification factor, rainfall volume, <br /> rainfall nitrate concentration, waste effluent quantity, and waste effluent nitrate concentration. <br /> The formula, assumptions and calculations used for the analysis are shown on Plates 7 and 8. <br /> The units of nitrate used in the mass balance equation are nitrate-N, whose maximum drinking <br /> water contaminant level is 10 mg/L. <br /> 2.1 Chemical and Physical Properties of Soil <br /> 2.1.1 Chemical and Physical Soil Properties <br /> For a discussion of on-site soil properties, refer to Section I.5. <br /> 2.1.2 Mass Transport Soil Properties <br /> The percolation tests have revealed that the soils are fairly permeable. These soils will allow <br /> moderate to rapid infiltration of water through the surface soils. The longer the effluent remains <br /> near the surface, the more treatment is enhanced due to natural processes within the soil. If <br /> the permeable soils exist to the depth of the ground water table, it is possible that surface <br /> contaminants may be transported fairly rapidly. <br /> .*44 <br /> 902 Industrial Way• Lodi,CA 95240•209.367.3701 • Fax 209.369.4228 02008 Neil O.Anderson&Associates,Inc <br />
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