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SR0082253 SSNL
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SR0082253 SSNL
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Last modified
12/21/2020 11:36:52 AM
Creation date
7/29/2020 2:21:57 PM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0082253
PE
2602
FACILITY_NAME
16042 E BAKER RD
STREET_NUMBER
16042
Direction
E
STREET_NAME
BAKER
STREET_TYPE
RD
City
LINDEN
Zip
95236
APN
09110008
ENTERED_DATE
6/25/2020 12:00:00 AM
SITE_LOCATION
16042 E BAKER RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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The existing septic systems were accounted for when determining the approximate nitrate <br /> concentration,the site could expect 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, if subdivided, will continue to be residential and agricultural. The existing parcel would be <br /> divided into a 2.3 acre lot and an unsurveyed remainder containing 37.7+/- acres. The proposed <br /> 2.3 acres will be used for rural residential purposes. For residential use,the approximate flow rate <br /> that is expected to be generated is between 50 to 70 gallons per person per day (Crites and <br /> Tchobanoglous). Calculating nitrate loads conservatively, the value of 70 gallons per person per <br /> day was used. This method is conservative as it does not include lateral dispersion or mixing of <br /> groundwater. These factors of safety are additional to the County's factor of safety. The residential <br /> homes both contain 3 bedrooms. The residential home is expected generate an approximate of 240 <br /> gallons of wastewater per day. <br /> The average total nitrogen concentration of domestic wastewater is about 20-85 mg/L-N, <br /> although 35-45 mg/L-N is a better approximation(Crites and Tchnobanglous). The value <br /> selected for this site was 35 mg/L-N. <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 low levels of denitrification. It is expected <br /> 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 Hanztch/Finnemore equation: <br /> Using the data mentioned within this report and the attached Soil Suitability Report the mass <br /> balance of nitrogen loading for this site was calculated, this was done using Hanztch/Finnemore <br /> formula. Based on the Hanztch/Finnemore equation each 5-acre parcel would contain a Nitrate <br /> Load(Nc) of 9.97 mg/L-N. The site would be able to sustain flow required for the existing house, <br /> a flow surpassing that amount could cause an impact to the site's nitrate load and surpass the <br /> maximum contaminant level (MCL) of 10.0 mg/L-N for Nitrate in drinking water. <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 possibilities that the <br /> percolating effluent could affect water conditions are present. The Hanztch/Finnemore equation's <br /> factor of lowers those risks,but no major additions should be made without an update to this report. <br /> 5 <br />
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