My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0005352_SSNL
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
M
>
MAGNOLIA
>
26534
>
2600 - Land Use Program
>
SU-00-04
>
SU0005352_SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
10/28/2020 11:05:38 AM
Creation date
9/6/2019 9:58:56 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0005352
PE
2611
FACILITY_NAME
SU-00-04
STREET_NUMBER
26534
Direction
E
STREET_NAME
MAGNOLIA
STREET_TYPE
AVE
City
ESCALON
APN
22+908018
ENTERED_DATE
8/29/2005 12:00:00 AM
SITE_LOCATION
26534 E MAGNOLIA AVE
QC Status
Approved
Scanner
SJGOV\wng
Supplemental fields
FilePath
\MIGRATIONS\M\MAGNOLIA\26534\SU-00-04_DV-00-02\SU0005352\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.
/
92
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
Mr.Raymond Vaz <br /> December 14,2001 <br /> Page 4 <br /> that the nitrate-nitrogen concentration of ground-water flow from up-gradient areas is lower."' <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 1 through 3. The units of nitrate used in the mass balance equation <br /> are nitrate-N whose maximum drinking water contaminate level is 10 mg/l. <br /> Nitrate Loading Analysis Variables and Assumptions <br /> Denitrification is one of many important processes occurring in septic systems whereby <br /> certain bacteria utilize the oxygen in the nitrate(NO3) and release nitrogen gas(NZ)to the <br /> atmosphere. Denitrification is expressed as a percentage, and the normally accepted range is 10 <br /> percent to 35 percent. Soils with higher clay content, moist soil conditions,high pH, and organic <br /> material denitrify about 35 percent of effluent and soils with very high sand content and fast <br /> percolation rates are estimated to denitrify effluent at a lower rate, about 10 percent to 15 <br /> percent.' Due to the predominance of dark colored sandy silt soils,the denitrification factor is <br /> estimated to be 25 percent. <br /> An estimate of the quantity and quality of rainfall and effluent is required for the analysis. <br /> The following information was used in the calculation. The deep percolation of rain was <br /> estimated to be 2.12 inches (Plate 1). The nitrate concentration of rain fall was estimated to be <br /> 0.17 mg/L-N.' <br /> The quantity of household waste water was estimated to be about 75 gallons per person <br /> per day. In a four bedroom residence, the typical occupancy of the main residence would <br /> probably range between two to five persons resulting in a daily waste water flow between 150 to <br /> 375 gallons per day(see Table 1). The potential impact of a legally permitted second dwelling <br /> unit whose size is allowed up to 500 sq-ft(3-bedroom home),must be accounted in this analysis <br /> per San Joaquin County PHS-EHD. The average nitrate concentration of the typical residential <br /> p[gROry <br /> r� <br /> O'j�4 <br />
The URL can be used to link to this page
Your browser does not support the video tag.