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SR0080264 SSNL
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Last modified
2/10/2022 11:10:17 AM
Creation date
11/19/2019 9:39:21 AM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0080264
PE
2602
STREET_NUMBER
16327
STREET_NAME
DIABLO
STREET_TYPE
CT
City
TRACY
Zip
95304
APN
20937019
ENTERED_DATE
2/27/2019 12:00:00 AM
SITE_LOCATION
16327 DIABLO CT
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Soil Suitability / Nitrate Loading Study <br /> Ernst Property Tracy, CA Irerracon <br /> February 21, 2019 Terracon Project No. NA197000 <br /> 2.3.2 Contribution of Rainfall <br /> An estimate of the quantity and quality of rainfall was required for the nitrate loading analysis. <br /> Average precipitation and potential evapotranspiration data was obtained from the California <br /> Irrigation Management Information System (CIMIS)from seven active and inactive CIMIS station <br /> in San Joaquin County including Manteca (070), Staten Island (242), Holt(248), Ripon (249), Lodi <br /> (042), Lodi West (166), and Tracy (167) over an approximately 34 year period. The estimate of <br /> deep percolation of rain is based on the average monthly precipitation of rain fall an <br /> evapotranspiration for San Joaquin County, California. The estimate first determines whether the <br /> average monthly precipitation exceeds average monthly potential evapotranspiration. If so, then <br /> the difference is potential deep percolation. This method does not consider runoff, although due <br /> relatively flat nature of the site runoff should be minimal. <br /> Table 4. <br /> Estimate of Deep Percolation of Rain 72 <br /> Location Average Deep Percolation of Rain <br /> San Joaquin County I 12.78 inches per year <br /> Based on this method, the average deep percolation of rain for San Joaquin County is estimated <br /> to be 12.78 inches/year. The nitrate concentration of rainfall is estimated to be 1 mg/L-N <br /> (Hantzsche and Finnemore, 1992). <br /> 2.3.3 Current On-Site Sources of Nitrate <br /> The current on-site sources of nitrate include the existing septic system and natural processes. <br /> 2.3.4 Future On-Site Sources of Nitrate <br /> Future on-site sources of nitrate are discussed in section 1.3.7. <br /> 2.3.4.1 Quantity and Quality of Wastewater from Project <br /> The following discussion is for determining the long-term wastewater flow generated from the <br /> proposed development for the nitrate loading analysis and should not be used for septic system <br /> design purposes. Typically, use estimates for the sizing of septic systems include a peak use <br /> factor, whereas the numbers discussed here are based on long-term averages. <br /> The estimated sewage flow rates for use categories are available from a number of references. <br /> The uses presented below were guided by the San Joaquin County On-Site Wastewater Disposal <br /> Standards (2003), Crites and Tchobanoglous (1998), and EPA (1980). Table 4-2 of the text from <br /> Crites and Tchobanoglous indicates that the typical residential use rate is 70-gallons per day per <br /> bedroom. The EPA Design Manual (Table 4-6) indicates the typical use rate is 45-gallons per <br /> day per resident. Based on a review of the USGS California Water Science Center California <br /> Responsive ■ Resourceful ■ Reliable. 13 <br />
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