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SR0076726_SSNL
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2600 - Land Use Program
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SR0076726_SSNL
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Entry Properties
Last modified
11/12/2020 8:37:02 AM
Creation date
9/4/2019 5:46:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0076726
PE
2601
STREET_NUMBER
21647
Direction
E
STREET_NAME
EASTERN HEIGHTS
STREET_TYPE
RD
City
LINDEN
Zip
95236
APN
10529020
ENTERED_DATE
2/2/2017 12:00:00 AM
SITE_LOCATION
21647 E EASTERN HEIGHTS RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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FilePath
\MIGRATIONS\E\EASTERN HEIGHTS\21647\BP-1700162\NIT STDY.PDF
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EHD - Public
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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 to <br /> 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 be <br /> used to calculate nitrate-nitrogen loading for this project (See Kaplan -Septic Systems Handbook, <br /> 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 ultimately to the Z, <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, which appear <br /> to be substantial, 2.) Variability in wastewater flows, nitrogen concentrations and dilution effects (i 3) <br /> from stormwater recharge, 3.) Changes in groundwater directional flow and elevation, 4.) <br /> Denitrification potential within the soil environment and within the confined and/or unconfined 0.Y) <br /> aquifers. <br /> The Hantzsche/Finnemore Formula is used in this report to predict the average resultant concentration <br /> of nitrate-nitrogen in effluent recharge water. As calculated below,the property has been assessed on a <br /> total areal loading basis correlated with the total projected yearly wastewater flow volumes calculated <br /> above. These two factors primarily estimate the average resultant concentration of nitrate-nitrogen in <br /> the recharge water. This concentration shall not exceed 10 ppm nitrate-nitrogen(45 ppm as nitrate). <br /> Calculated nitrate-nitrogen loading from the entire subject property: <br /> INw G - d) + R Nb <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 /> Values and Assumptions: <br /> I=276 x365 d/yr= 100,740 gals=total WW/yr— 13.500 cu ft = 1.86 in/yr <br /> 2.00 Ac x 43,560 sq ft/Ac x (1 ft/12 in) <br /> v r�33i33 <br /> l2v �l . GL LGGf. Page 4 of 7 �_Ji <br /> 52211 .02 Chesney Consulting <br />
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