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COMPLIANCE INFO_NL STDY
Environmental Health - Public
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4200 – Liquid Waste Program
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PR0516930
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COMPLIANCE INFO_NL STDY
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Last modified
12/4/2020 9:22:10 AM
Creation date
8/5/2020 10:01:23 AM
Metadata
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Template:
EHD - Public
ProgramCode
4200 – Liquid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
NL STDY
RECORD_ID
PR0516930
PE
4242
FACILITY_ID
FA0012932
FACILITY_NAME
NAVARRA BROS
STREET_NUMBER
23833
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
25014014
CURRENT_STATUS
01
SITE_LOCATION
23833 CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\4200 - Liquid Waste\C\CHRISMAN\23833\PR0516930\NL STDY.PDF
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EHD - Public
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From the anticipated wastewater characteristics described above, the nitrogen emanating from the <br /> project may be at a higher concentration than what would normally be found in a typical <br /> domestic or household system. This can be attributed to the lack of a dilution effect that <br /> graywater from showers, laundry, etc. would provide. The scientific literature cites nitrogen <br /> concentrations in residential septic effluent typically ranging from 17 mg NIL for basins, sinks, <br /> etc. to 140 mg NIL for toilet wastes. Therefore, considering a 70/30 percent usage for toilet <br /> water volume and sink water volume, respectively, a value of 103 mg NIL of septic effluent will <br /> be used to calculate nitrate-nitrogen loading for this project. <br /> B. PREDICTED NITRATE-NITROGEN LOADING <br /> The calculated or estimated nitrate-nitrogen impact to the soil and ultimately to the groundwater <br /> is difficult to determine due to the number of variables involved. These variables include 1.)past <br /> installation methods of the on-site septic systems, 2.) future replacement methods for failed <br /> systems, 3.) impact from upgradient nitrate sources, 4.) variability in wastewater flows, nitrogen <br /> concentrations and dilution effects, 5.) changes in groundwater directional flow and elevation, G.) <br /> denitrification potential and landscape uptake of nitrogen, and 7.) proposed installation of a <br /> wastewater treatment system to mitigate nitrate impact. <br /> The following nitrate-nitrogen loading calculations are presented under two scenarios. The first <br /> loading projections are based on using conventional septic systems (septic tank and Ieachfields) <br /> throughout the entire, completed project. This will present comparison data between the use of <br /> traditional systems, versus treating a percentage of the total wastewater originating from the <br /> project as a whole. <br /> The second loading calculations factor in an anticipated reduction in loading through the use of <br /> an on-site wastewater treatment system and utilization of landscaping as a nitrogen uptake <br /> medium. This estimated nitrogen loading will be added to the remaining projected loading from <br /> the conventional systems north of Carmelo Avenue. <br /> There are various scientific methods to estimate nitrate-nitrogen loading. This report uses the <br /> Hantzsche/Finnemore Formula to predict the average concentration of nitrate-nitrogen in effluent <br /> recharge water. <br /> PREDICTED NITRATE-NITROGEN LOADING FROM A COMPLETELY BUILT- <br /> OUT PROJECT USING CONVENTIONAL SEPTIC SYSTEMS: <br /> HANTZSCHEIFINNEMORE EQUATION <br /> INW Q - d, +R Nb <br /> Nr (I+ R) <br /> Chesney Consulting <br />
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