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SU0006046 SSNL
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SU0006046 SSNL
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Last modified
5/7/2020 11:32:03 AM
Creation date
9/8/2019 12:42:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0006046
PE
2632
FACILITY_NAME
PA-0600237
STREET_NUMBER
7087
Direction
E
STREET_NAME
PELTIER
STREET_TYPE
RD
City
ACAMPO
Zip
95220
APN
00526041
ENTERED_DATE
5/17/2006 12:00:00 AM
SITE_LOCATION
7087 E PELTIER RD
RECEIVED_DATE
5/16/2006 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\P\PELTIER\7087\PA-0600237\SU0006046\SS STDY.PDF \MIGRATIONS\P\PELTIER\7087\PA-0600237\SU0006046\NL STDY.PDF
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EHD - Public
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i <br /> ir. Ifto, N-./ <br /> July 28,2006 <br /> NOA Project Number: E06068A <br /> bob J3.3 Current and Future On-Site Ground Water Uses <br /> A description of the existing wells on the Site is included in Section 4.3 of the SSS. Ground water is <br /> currently used for agricultural and domestic purposes. <br /> ion 4.0 SOURCES AND IMPACT OF NITRATE TO GROUND WATER <br /> /4.1 Current Off-Site Sources of Nitrate <br /> Septic systems, agriculture, and dairies in the area may be the most significant sources of nitrate. <br /> Septic tank use in the vicinity is discussed in Section 3.4 was found to be moderate. The ground <br /> water sample, des sse ctions 4.3 through 4.6 of the SSS,was found to have a nitrate <br /> concentration of 9 mg/L- 03. This concentration indicates that the ground water aquifer is <br /> likely not experiencing rutrate leaching from various sources in the area over the long term. <br /> too <br /> 4.2 Contribution of Rainfall <br /> An estimate of the quantity and quality of rainfall was required for the nitrate loading analysis. The <br /> estimate of deep percolation of rain is based on the average monthly precipitation of rainfall and <br /> evapotranspiration for Lodi, California. The estimate first determines whether the average monthly <br /> precipitation exceeds average monthly potential evapotranspiration. If so, then the difference is <br /> potential deep percolation. This method does not consider runoff. See Plate 9 for the data and <br /> calculation. <br /> /Average potential evapotranspiration and average rainfall data was obtained from the California <br /> Irrigation Management Information System (CIMIS). The data from January 1988 to December <br /> �- 2004 was used for the calculation. <br /> Based on this method, the average deep percolation of rain for the Lodi area is estimated to be 5.76 <br /> •. inches. The nitrate concentration of rain fall was estimated to be 1 mg/L-N (Hantzsche and <br /> Finnemore, 1992). <br /> >r �' 4.3 Current On-Site Sources of Nitrate <br /> Current on-site sources of nitrate include the current septic systems for the administrative buildings. <br /> ✓4.4 Future On-Site Sources of Nitrate <br /> r. 14 4.1 Quantity and Quality ofDomestic Wastewater From Proposed Project <br /> The following discussion is for determining the long-term waste water flow generated from the <br /> 3 <br /> July 28, 2006 <br /> NOA Project Number: E06068A <br /> ✓proposed residences for the nitrate loading analysis and should not be used for septic system design <br /> purposes. Typically, use estimates for the sizing of septic systems include a peak use factor,whereas <br /> the numbers discussed here are based on long-term averages. <br /> /The existing and proposed administrative buildings are proposed to hav 25 employees per and <br /> 1/ will not serve customers. We understand that the offices are planned to be o ately 10 <br /> hours per day, five days per week. <br /> The estimated sewage flow rates for use categories are available from a number of references. The <br /> uses presented below were guided by the San Joaquin County On-Site W>astewater Disposal Standards <br /> (2003), Crites and Tchobanoglous (1998), and EPA (1980). The references indicate that 14 gallons <br /> for each employee is typical for an office worker. (Crites and Tchobanoglous, 1998). <br /> /The following tables presents the septic waste water uses associated with the Site. The rates <br /> presented from the references provide general guidance but do not always reflect a match in usage. <br /> Careful examination,professional judgement, and experience are necessary to select a reasonable <br /> flow rate estimate. The flow rates selected for maximum uses associated with this project are <br /> presented in the following table. <br /> �- Table 1. <br /> Typical Quantity of Effluent <br /> Total People per Average Quantity per Average Daily Flow <br /> Category Day Person Per Parcel <br /> Commercial 25 14 al/da /em to ee 25 employees* 14 d = 350 gpd <br /> ` Note —gpd is gallons per day. <br /> Vfor the subject property, the total daily waste water quantity is 350 gallons per day.A five-sevenths <br /> Lconversion was used to account for a five day work week. Five-sevenths of 350 gallons ler day is <br /> 250 gallons per day average. <br /> ` rThe average total nitrogen concentration of domestic waste water is normally considered to be <br /> 20-85 mg/L-N with 35 to 45 mg/L-N being typical (Crites and Tchobanoglous, 1998). It is <br /> estimated that commercial use will have higher concentrations of total nitrogen when compared to <br /> ` residential use. It is estimated that-the average concentration for total nitrogen in waste water for <br /> the project is approximateii.$ mg/Lover the long term. <br /> 6. <br /> ow <br /> bw <br /> 4 <br /> v <br />
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