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SU0002478_SSNL
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SU0002478_SSNL
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Entry Properties
Last modified
11/19/2024 1:52:11 PM
Creation date
9/8/2019 12:51:02 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002478
PE
2633
FACILITY_NAME
SA-01-41
STREET_NUMBER
11374
Direction
S
STREET_NAME
STATE ROUTE 99
City
MANTECA
APN
20103019
ENTERED_DATE
10/29/2001 12:00:00 AM
SITE_LOCATION
11374 S HWY 99
QC Status
Approved
Scanner
SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\N\HWY 99\11374\SA-01-41\SU0002478\NL STDY.PDF
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EHD - Public
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S GNET _.Vd STL Project No. 0010771 <br /> 7z-,sil 1 Las Appendix D <br /> gbPage D.1 <br /> APPENDIX D <br /> ` NITRATE LOADING STUDY <br /> The principal concern with respect to the build-up of nitrates within the groundwater is <br /> methemoglobinemia, which is of particular concern with infant children. Methemoglobinemia, also <br /> known as "blue baby syndrome," occurs when bacteria in the digestive system transforms nitrate to <br /> nitrite and the nitrite oxidizes iron in hemoglobin of red blood cells to form methemoglobin. <br /> Methemoglobin lacks the capacity to carry oxygen and the resulting condition can ultimately lead to <br /> .. death if undetected. Therefore, the Environmental Protection Agency has set the maximum contaminant <br /> level(MCL)for drinking water of 10 mg/L or 10 parts per million for nitrate-nitrogen. <br /> Because of the concern for nitrate leaching into the groundwater system, a nitrate loading study was <br /> performed to estimate the average nitrate concentration of percolating water for the subject site. The <br /> sources included in our loading study included the percolation from the on-site sewage disposal system <br /> L and recharge due to rainfall. <br /> To this end, we utilized a simple mass balance formula, often referred to as the Hantzsche and Finnemore <br /> Equation. The equation is somewhat conservative and is often thought of as a worst-case approximation <br /> ` for the chronic effects of groundwater-laden nitrate-nitrogen resulting from the combined effect of <br /> rainwater and septic system percolations. The equation takes into consideration the development area <br /> and land use, soil chemistry, rainfall criteria and sewage system effluent characteristics. The Hantzsche <br /> ` equation and design parameters utilized herein are as follows: <br /> Nitrate-nitrogen (Nc)_(I Nw( 1-D)+R Nb)/(I+R) <br /> Where: I = Amount of wastewater entering subsurface for subject area in/year <br /> Nw= Nitrate-nitrogen concentration in wastewater (mg/L) <br /> D = denitrification as a percent of original concentration (%) <br /> R= Recharge due to precipitation (in/year) <br /> Nb = Background concentration of nitrate-nitrogen in rainfall (mg/L) <br /> The amount of wastewater that enters the subsurface was determined on the basis of the following <br /> criteria: <br /> The per capita flow to a septic tank is 80 gallons per day (US EPA Publication No. 625/1-80- <br /> ` 012, Design Manual for On-Site Wastewater Treatment and Disposal Systems, page 51, 1980; <br /> Kaplan O. Benjamin, Septic Systems Handbook, pages 147-148, 1988, Lewis Publishers). <br /> ` e have assumed 2.5 residents per household at 80 gpd, a working staff of 4 persons at 15 <br /> gpd, and 10 customers per day at 5 gpd, resultin i a net average of 19 gpd for 16.5 persons. <br /> The averse rate of discharge of nitrogen per person per da is 15 rams as N (Kaplan, O. 3' <br /> 8 g g P P P Y � g ( P <br /> ` Benjamin, Septic Systems Handbook, pages 147-149, 1998, Lewis Publishers; State Water <br /> Resources Control Board, Identification and Evaluation of Methods for Determining Sources of <br /> Nitrate Contamination of Groundwater, page 18, 1994). <br /> r <br /> 1417 No. Market Blvd., Suite 1 • Sacramento,CA 95834 . (916)568-5858 • Fax: (916)568-5813 <br />
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