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SU0011793_SSNL
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SU0011793_SSNL
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Last modified
11/19/2024 4:00:00 PM
Creation date
9/8/2019 12:32:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0011793
PE
2691
FACILITY_NAME
PA-1800112
STREET_NUMBER
11150
Direction
E
STREET_NAME
STATE ROUTE 120
City
MANTECA
Zip
95336-
APN
22803028
ENTERED_DATE
5/10/2018 12:00:00 AM
SITE_LOCATION
11150 E HWY 120
RECEIVED_DATE
5/8/2018 12:00:00 AM
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\O\HWY 120\11150\PA-1800112\SU0011793\SS_NL STUDY .PDF
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EHD - Public
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' Soil Suitability/Nitrate Loading Study Irerracon <br /> Proposed Global Carrier Inc. ■ Manteca, California <br /> August 8, 2018 n Terracon Project No. NA187034 <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 groundwater nitrate impacts on an area- <br /> wide basis. <br /> Hantzsche and Finnemore found that over a long period of time, water quality in the upper <br /> saturated groundwater 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 planners <br /> and local officials but with some real limitations. In their article published in Ground Water, <br /> Hantzsche and Finnemore mention that "...the equation ignores dispersion, lateral flow, and <br /> mixing with groundwater flow from up-gradient areas. These processes would generally <br /> contribute to additional reduction of nitrate-nitrogen concentrations in groundwater to the extent <br /> that the nitrate-nitrogen concentration of groundwater flow from up-gradient areas is lower." <br /> The Hantzsche and Finnemore approach is "...a conservative (worst case)first approximation of <br /> groundwater nitrate-nitrogen concentration resulting from the combined effect of on-site sewage <br /> disposal systems and precipitation. This (the equation and approach) is for estimation of long- <br /> term effect(i.e., over years)on groundwater quality, and is not intended for prediction of seasonal <br /> 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. The <br /> formula, assumptions and calculations used for the analysis are shown in Appendix B. The units <br /> of nitrate used in the mass balance equation are nitrate-N, of which the maximum drinking water <br /> contaminant level (MCL) 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 1.5. <br /> 2.1.2 Mass Transport Soil Properties <br /> The percolation test has revealed that soils between 0 and 3.5 feet bgs are permeable and will <br /> allow for sufficient infiltration of water. In general, the longer the effluent remains near the surface, <br /> the more treatment is enhanced due to natural processes within the soil. The high permeability <br /> of the silty sandy soils indicates nutrients such as nitrates may leach through the site soils more <br /> rapidly than soils with clay strata. <br /> Responsive■ Resourceful ■ Reliable 13 <br />
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