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SU0006750 SSNL
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SU0006750 SSNL
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Last modified
5/7/2020 11:32:42 AM
Creation date
9/8/2019 1:02:32 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0006750
PE
2632
FACILITY_NAME
PA-0700438
STREET_NUMBER
3836
Direction
N
STREET_NAME
NEWTON
STREET_TYPE
RD
City
STOCKTON
APN
13206002
ENTERED_DATE
10/2/2007 12:00:00 AM
SITE_LOCATION
3836 N NEWTON RD
RECEIVED_DATE
10/1/2007 12:00:00 AM
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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\MIGRATIONS\N\NEWTON\3836\PA-0700438\SU0006750\NL STDY.PDF
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EHD - Public
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Traylor Shea Precast Page 11 of 14 <br /> Our Project Number: E071WB i <br /> November 29, 2007 <br /> v <br /> For Phase I of the project, the total daily waste water quantity is 371 gallons per day (gpd). <br /> The flow rates selected for the uses associated with Phase II of this project are presented next. <br /> Table 7. <br /> Typical Quantity of Effluent Phase U). <br /> Category Total People Average Quantity per Average Daily Flow per Parcel <br /> per Day Person <br /> Employees 46 13 gal/day/employee (46 employees * 13 gpd * 7) 427 gpd <br /> Note: gpd is gallons per day. <br /> _ For Phase II of the project, the total daily waste water quantity is 427 gallons per day. <br /> The 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 <br /> to residential use. It is estimated that the average concentration for total nitrogen in waste <br /> water for the project is approximately 85 mg/L-N over the long term. <br /> I1.3.4.2 Denitrification Estimate <br /> Denitrification is an important process which occurs within the leach field whereby certain <br /> bacteria utilize the oxygen in the nitrate (NO3) and release nitrogen gas (NZ) to the atmosphere. <br /> Denitrification is expressed as a percentage, and the normally accepted range is 10 percent to <br /> 35 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. A typical denitrification <br /> factor of 25 percent was selected for the Site because of the fine grained nature of the soils. <br /> II.3.5 Nitrate Loading Scenario <br /> A nitrate loading scenario was performed to determine the impact from the proposed project. <br /> The scenario utilizes the variables discussed previously which represent the estimated <br /> conditions and uses associated with this project. The following table presents a summary of the <br /> nitrate loading calculations for the site, as presented in Plates 10 and 11. <br /> Table 8. <br /> S frimary of Nitrate Mass Balance Equation. <br /> Result Average Effluent Leachfield Deep <br /> Phase of Concentration Percolation <br /> (Nc)* Acres(A) Daily Flow Denitrification <br /> Project (mg/1-N) (Q)(gpd) (Nw) (d) of Rainfall <br /> (m9/�-N) (R)(in) ('i 5 <br /> Phase I 7.9 8.58 371 85 25% 4.67 <br /> Phase II 8.9 8.58 427 85 25% 1 4.67 <br /> * Maximum contaminant level (MCL)for nitrate in drinking water is 10 mg/L-N. <br /> V <br /> 902 Industrial Way•Lodi,CA 95240•209.367.3701 •Fax 209.369.4228 ©2007 Neil O.Anderson&Associates,Inc <br />
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