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SU0011318 SSNL
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SU0011318 SSNL
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Last modified
5/7/2020 11:35:05 AM
Creation date
9/5/2019 11:18:11 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0011318
PE
2633
FACILITY_NAME
PA-1700072
STREET_NUMBER
20500
Direction
S
STREET_NAME
HOLLY
STREET_TYPE
DR
City
TRACY
Zip
95304-
APN
21216010
ENTERED_DATE
4/17/2017 12:00:00 AM
SITE_LOCATION
20500 S HOLLY DR
RECEIVED_DATE
4/17/2017 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\H\HOLLY\20500\PA-1700072\SU0011318\SS_NL STUDY.PDF
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EHD - Public
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B. CALCULATED NITRATE-NITROGEN LOADING <br /> NLS§3.4,3.5,3.6. The calculated nitrate-nitrogen impact to the soil and ultimately 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 nitrate sources, 2.) Variability in <br /> wastewater flows, effluent nitrogen concentrations and dilution effects from stormwater recharge, <br /> 3.) Changes in groundwater directional flow and elevation, 4.) And of significant importance is not <br /> only the denitrification potential of the indigenous clays, but equally important is the diminished <br /> nitrification potential within the clay soil environment. The extremely small pore space within the <br /> high clay content soil significantly reduces oxygen content, thus impeding nitrification. <br /> The Hantzsche/Finnemore Formula is used below to predict the average resultant concentration of <br /> nitrate-nitrogen in effluent recharge water from the proposed wastewater treatment and management <br /> system. The calculations are based on a total areal loading basis previously referenced, correlated <br /> with the annually projected wastewater flaws of 416,000 gpy. These two factors primarily estimate <br /> the average resultant concentration of nitrate-nitrogen in the recharge effluent. This concentration <br /> cannot exceed 10 ppm nitrate-nitrogen(45 ppm as nitrate). <br /> CALCULATED NITRATE-NITROGEN LOADING FROM THE COMBINED ON-SITE <br /> RESTROOMS FOR THE ENTIRE SUBJECT PARCEL: <br /> HANTZSCHE/FINNEMORE EQUATION <br /> 2jµ,(1 - d) + 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 combined loss in theliigh clay content soil due to: <br /> 1.) Prevention of nitrification and 2.)The denitri cation of ni to molecules that may form. <br /> R = Average recharge rate of rainfall - inches per yr NLS§3.2 <br /> Nb = Background nitrate-nitrogen concentration of rainfallrecha e,exclusive of wastewater influences <br /> (ppm NO3-N). <br /> Values and Assumptions: <br /> I—416,000 gals=total WW/Yr=55.615 cu ft =0.0933 in/yr <br /> 164.28 Ac x 43,560 sq ft/Ac x(1 ft/12 in) <br /> Nw= 62 mg N/L <br /> d = Assume 25%due to the high percentage of clay soil(28%)throughout the soil profile that not only <br /> mitigates nitrification,but also promotes denitrification of nitrate molecules that may form, <br /> R = 9.5 in/yr. <br /> (Nb= Assumed to be 0.1 ppm NO3-N <br /> Page -7- <br /> Chesney Consulting <br />
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