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SR0080885 SSNL
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SR0080885 SSNL
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Last modified
11/19/2019 9:48:46 AM
Creation date
11/19/2019 9:05:58 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0080885
PE
2602
FACILITY_NAME
DEPARTMENT OF ENERGY - LAWRENCE LIVERMORE NATIONAL LAB C/O ADA CHAN (SITE REP)
STREET_NUMBER
15999
Direction
W
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95377
APN
25114005
ENTERED_DATE
7/15/2019 12:00:00 AM
SITE_LOCATION
15999 W CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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15999 W CORRAL HOLLOW RD Project No.2019-00027 Page 18 <br /> For the site,the total daily toilet use contributing wastewater quantity is 2,566 gallons per day.The <br /> average total nitrogen concentration of domestic wastewater is normally considered to be 20-85 <br /> m�- N_with 35 to 45 mg/L-N being typical (Crites and Tchobanoglous, 1998). To be conservative, <br /> >'we have esti m ted that for this site a commercial wastewater concentration will be approximately <br /> 85 mg/L-N. <br /> 4.4.2 :Denitrification Estimate <br /> Denitrification is an important process which occurs within the leach field whereby certain bacteria <br /> utilize the oxygen in the nitrate (NO3) 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 denitrify <br /> by about 35 percetp-arid'sgils with high sand content and fast percolation rates are estimated to <br /> denitrify at a low�r,rate,about 10 percent to 15 percent.To be conservative,and based on the sandy <br /> soils,w have used,a 10 percent denitrification value. <br /> 4.5 Nitrate Loading <br /> A nitrate loading scenario was performed to determine the impact from the proposed project. The <br /> scenario utilizes the variables discussed previously which represent the estimated conditions and <br /> uses associated with this project. The following table presents a summary of the nitrate loading <br /> calculation for the parcel. <br /> Table 4. <br /> Summary of Nitrate Mass Balance Anal sis. <br /> Parcel Result Acres Average Daily Effluent Leachfield Deep <br /> (Nc)* (A) Flow(Q) Concen- Denitrifi- Percolation of <br /> (mg/L-N) (gpd) tration cation(d) Rainfall (R) <br /> (Nw) (Plate 9) (in.) <br /> (mg/L-N) <br /> 1 1.2 5,753 2,566 85.00 1 10% 1 2.52 <br /> * Maximum contaminant level (MCL) for nitrate in drinking water is 10 mg/L-N. <br /> 4.6 Impact of Nitrate Loading to Nearby Water Sources <br /> Based on the methods and assumptions described, in addition to our professional judgement and <br /> geologic setting,we believe the proposed projects will not cause a build-up of nitrate in the ground <br /> water above 10 mg/L-N over the long term. <br /> Based on the relatively flat topography of the site,we do not foresee percolating effluent affecting <br /> any surface water resources. <br /> �V" <br /> Petralogix Engineering,Inc. rt , <br /> 26675 Bruella Road,Galt,Ca 95632k, �1 a��r <br /> (209)-406-5729 !A{�tb4ieF;` <br /> .phr^ <br /> wwwetralogix.corn tk " <br />
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