My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0002158 SSNL
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
P
>
PONDEROSA
>
7960
>
2600 - Land Use Program
>
UP-01-05
>
SU0002158 SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/7/2020 11:29:03 AM
Creation date
9/8/2019 12:46:30 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002158
PE
2626
FACILITY_NAME
UP-01-05
STREET_NUMBER
7960
Direction
S
STREET_NAME
PONDEROSA
STREET_TYPE
ST
City
FRENCH CAMP
ENTERED_DATE
10/23/2001 12:00:00 AM
SITE_LOCATION
7960 S PONDEROSA ST
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\P\PONDEROSA\7960\UP-01-05\SU0002158\NL STDY.PDF
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
38
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
September 20,2001 <br /> Job Number: LGO1-098 <br /> Page 9 <br /> The Hantzsche and Fennemore equation'provides "...a conservative(worst case) first <br /> approximation of ground-water nitrate-nitrogen concentration resulting from the combined effect <br /> of on-site sewage disposal systems and precipitation. This (the equation and approach) is for <br /> _ estimation of long-term effect(i.e., over years) on ground-water quality, and is not intended for <br /> prediction of seasonal changes." <br /> The Hantzsche and Fennemore' equation takes into account development area, soil <br /> denitrification factor, rainfall volume, rainfall nitrate concentration, the waste effluent quantity, <br /> and waste effluent nitrate concentration. The formula, assumptions and calculations used for the <br /> analysis are shown on Plates 8 and 9. The units of nitrate used in the mass balance equation are <br /> nitrate-N whose maximum drinking water contaminate level is 10 mg/l. <br /> — Denitrification is an important process in septic systems that normally occurs in the leach <br /> line whereby certain bacteria utilize the oxygen in the nitrate(NO3) and release nitrogen gas (Nz) <br /> to the atmosphere. Denitrification is expressed as a percentage, and the normally accepted range <br /> is 10 percent to 35 percent. Soils with higher clay content, moist soil conditions, high pH, and <br /> organic material denitrify about 35 percent and soils with very high sand content and fast <br /> percolation rates are estimated to denitrify at a lower rate, about 10 percent to 15 percent. Due to <br /> the occurrence of silty sand surface soils, the denitrification factor is estimated to be about 15 <br /> percent in a standard septic system leach line. <br /> An estimate of the quantity and quality of effluent is required for the analysis therefore <br /> the following information was used in the calculation. The deep percolation of rain was <br /> estimated to be 5.01 inches and the calculation is shown on Plate 8. The nitrate concentration of <br /> rain fall was estimated to be 0.17 mg/L-N.7 <br /> Nitrates from Septic System <br /> The quantity of effluent waste water was estimated to be 5 gallons per person per da . <br /> Table 6 presents the highest anticipated use for the facility. The facility will most likely not be <br /> operating at this high occupancy during the average year. The average nitrate concentration of <br /> the typical septic waste is normally considered to be`45 mg/L-N.' u X �� ��i+✓ <br /> s t d --K t6; <br /> s Otis,R.J.,Boyle,W.C., 1980,Design manual,onsite wastewater treatment and disposal systems:U.S. <br /> Environmental Protection Agency,EPA 625/1-80-012. (Seepage 100,table 6-1). <br /> ?OE4J0 <br /> ♦ 1- <br /> Z ' <br /> G A <br /> 1JS OG♦ <br />
The URL can be used to link to this page
Your browser does not support the video tag.