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SU0003611 SSNL
Environmental Health - Public
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SU0003611 SSNL
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Last modified
5/7/2020 11:30:05 AM
Creation date
9/8/2019 1:04:07 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0003611
PE
2690
FACILITY_NAME
LA-01-102
STREET_NUMBER
16910
Direction
S
STREET_NAME
NORTH RIPON
STREET_TYPE
RD
City
RIPON
APN
20308022
ENTERED_DATE
5/7/2004 12:00:00 AM
SITE_LOCATION
16910 S NORTH RIPON RD
RECEIVED_DATE
2/19/2002 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\N\NORTH RIPON\16910\LA-01-102\SU0003611\NL_SS STDY.PDF
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EHD - Public
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July 21,2003 <br /> Job Number:LG03-120 <br /> Page 10 <br /> 7.3 Quantity and Quality of Deep Percolating Rain Water <br /> An estimate of the quantity and quality of rainfall was required for the analysis. The weather <br /> station information for Stockton's precipitation and evaporation was used to estimate the deep <br /> percolation of rain for the site located in Ripon. The deep percolation of rain was estimated to be <br /> 5.01 inches. Please refer to Plate 1 for details regarding the deep percolation of rain. The nitrate <br /> concentration of rain fall was estimated to be 1 mg/L-N.' <br /> 7.4 Denitrification Estimate <br /> Denitrification is an important process which occurs within the leach field whereby certain <br /> bacteria utilize the oxygen in the nitrate(NO ) and release nitrogen gas (N2) to the atmosphere. <br /> Denitrification is expressed as a percentage, and the normally accepted range is 10 percent to 35 <br /> percent. Soils with higher clay content, moist soil conditions, high pH, and organic material <br /> denitrify by about 35 percent and soils with high sand content and fast percolation rates are <br /> estimated to denitrify at a lower rate, about 10 percent to 15 percent. Due to the sandy soils which <br /> exist on the site, the denitrification factor is estimated to be about 10 percent. <br /> 7.5 Nitrate Loading Scenarios '--- <br /> Two nitrate loading scenarios were performed to determine the impact for both the large <br /> designated remainder parcel of 79.8 acres and the smaller 2.0-acre parcels. For each scenario, the <br /> previously described assumptions were unitized in the Hantzshe and Finnemore equation. The <br /> likely added contribution from future agriculture was not considered however it is expected to <br /> also contribute to some degree. <br /> 9 Hantzshe N.N.,Finnemore,E.J. 1991,Predicating Ground-Water Nitrate-Nitrogen Impacts. Ground <br /> Water,Vol. 30,No.4. <br /> nEll <br />
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