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SR0084207_SSNL
Environmental Health - Public
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SR0084207_SSNL
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Last modified
10/29/2021 4:27:14 PM
Creation date
10/29/2021 4:15:58 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0084207
PE
2602
FACILITY_NAME
2658 S DRAIS AVE
STREET_NUMBER
2658
Direction
S
STREET_NAME
DRAIS
STREET_TYPE
AVE
City
STOCKTON
Zip
95215
APN
18323014
ENTERED_DATE
9/14/2021 12:00:00 AM
SITE_LOCATION
2658 S DRAIS AVE
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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5.3 Description of all current on-site sources of nitrate to soil and groundwater and the <br />contribution of nitrate load from these sources to the project site: The sources of nitrate is the <br />existing septic system in use by an existing parcel for residential uses. The existing septic system <br />was accounted for when determining the approximate nitrate concentration, the site is expected to <br />maintain its current flow with the proposed development. <br />5.4 Discussion of all proposed future on-site sources of nitrate to soil and groundwater and <br />the contribution of nitrate load from these sources to the project site: The future use of the <br />site will remain consistent. The existing residence with 1 bedroom was used to approximate the <br />amount of people that could generate waste water flow. It was conservatively assumed that 100 <br />gal/day would be generated for the first bedroom and 50 gal/day subsequently for every other <br />bedroom, generating at a total of 100 gallons/day. The site is expected to be able to handle up to <br />6350 gallons/day, making the current flows sustainable. <br />Similarly, there is no residences or definitive source of nitrates on the second 60 acre parcel; but <br />250 gal/day were used in assuming a residence could be built in the future. The 60 acre parcel <br />would have no problem with these small flows, considering peak flow rate allowed is 6350 <br />gal/day, but no major additions should be made without update to this report. <br />The average total nitrogen concentration of domestic wastewater is about 20-85mg/L-N, <br />although 35-45mg/L-N is a better approximation (Crites and Tchnobanglous). The value selected <br />for this site was 45mg/L-N assuming this site shall experience a larger concentration. <br />The site will experience a process of denitrification as the soil naturally treats surface material <br />through natural forms. Denitrification is a process that occurs when bacteria uses oxygen in the <br />nitrate (NO3) and release nitrogen (N2) into the atmosphere. Denitrification can be variable to the <br />type of soils, chemical properties, moisture content and other variables. Based on the sandy loams <br />on site and the high percolation rates, this site's soil has moderate levels of denitrification. It is <br />expected that a site with soil of these characteristics shall have approximately about 10-15% of <br />denitrification. The value used for this site was 15%. <br />5.5 Calculate mass balance of nitrogen loading considering all potential sources identified <br />using Hanzteh/Finnemore equation: Using the data mentioned within this report and the <br />attached Soil Suitability Study, the mass balance of nitrogen loading for this site was calculated. <br />This was done using Hanztch/Finnemore formula. Based on the Hanztch/Finnemore equation, the <br />two 60 acre sites would contain a Nitrate Load (Nc) of 9.97 mg/L-N when the site is generating its <br />peak flows. (6350 gallons/day) <br />6.0 Discussion of nitrate loading results relative to proposed method of <br />wastewater disposal <br />6.1 Discussion of total nitrate impact from proposed project: There are very low possibilities <br />that the percolating effluent could affect ground water conditions. <br />
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