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SR0078823 SSNL
Environmental Health - Public
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2600 - Land Use Program
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SR0078823 SSNL
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Entry Properties
Last modified
1/15/2020 2:28:37 PM
Creation date
9/4/2019 11:15:23 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0078823
PE
2601
STREET_NUMBER
31000
Direction
S
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25325005,19
ENTERED_DATE
3/7/2018 12:00:00 AM
SITE_LOCATION
31000 S CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\sballwahn
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FilePath
\MIGRATIONS\C\CHRISMAN\31000\NL STUDY .PDF
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EHD - Public
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FFThepecifies that each bedroom has the potential for two people,therefore an ADF of 140 <br /> py. As referenced,the existing house has four bedrooms and the proposed second unit <br /> ill have three bedrooms, for a total of seven bedrooms. Therefore, total flow volume <br /> = 7 x 140= 980 gallons wastewater/day. <br /> Wastewater Characteristics <br /> Blackwater will originate from toilets and graywater from showers, laundry, teeth brushing, <br /> dishwashing and hand washing. Additional wastewater constituents may consist of other liquids <br /> to the system, such as coffee,juices, etc. <br /> The scientific literature cites nitrogen concentrations in domestic septic effluent typically ranging <br /> from 17 mg N/L for basins, sinks, etc. to 140 mg N/L for toilet wastes. Therefore,taking a <br /> composite of these values, a nitrogen concentration of 62 mg N/L within the septic effluent will <br /> be used to calculate nitrate-nitrogen loading for this project(See Kaplan -Septic Systems <br /> Handbook, Pg. 147). <br /> CALCULATED NITRATE-NITROGEN LOADING <br /> NLS§3.3,3.4,3.5,3.6. The calculated nitrate-nitrogen impact to the soil and potentially to the <br /> groundwater is difficult to determine due to the large number of variables involved and variables <br /> unknown at this time. These include: 1.) Impact from upgradient agricultural sources, 2.) <br /> Variability in wastewater flows, nitrogen concentrations and dilution effects from stormwater <br /> recharge, 3.) Changes in groundwater directional flow and elevation, 4.) Denitrification potential <br /> within the clay soil environment and within the confined and/or unconfined aquifers. <br /> The Hantzsche/Finnemore Formula is used in this report to predict the average resultant <br /> concentration of nitrate-nitrogen in effluent recharge water. As calculated below,the property has <br /> been assessed on a total areal loading basis correlated with the total projected yearly wastewater <br /> flow volumes calculated above. These two factors primarily estimate the average resultant <br /> concentration of nitrate-nitrogen in the recharge water. This concentration should not exceed 10 <br /> ppm nitrate-nitrogen(45 ppm as nitrate). <br /> Calculated nitrate-nitrozen loading from the entire subject property: <br /> INwLL- _dA+ RNb <br /> Nr= (I + R) <br /> Where: <br /> Nr = Resultant average concentration of nitrate-nitrogen in recharge water-(ppm NO3-N) <br /> I = Volume rate of wastewater entering the soil averaged over the gross developed area in inches per yr <br /> Nw = Total nitrogen concentration of wastewater in mg N/L <br /> d = Fraction(%)of nitrate-nitrogen loss due to denitrification in the soil <br /> R = Average recharge rate of rainfall - inches per yr NLS§3.2 <br /> Nb = Background nitrate-nitrogen concentration of rainfall recharge, exclusive of wastewater influences <br /> (ppm NO3-N), <br /> Page 5 of 12 <br /> Chesney Consulting <br />
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