My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SR0084984_SSNL
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
A
>
ACAMPO
>
5800
>
2600 - Land Use Program
>
SR0084984_SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/6/2022 8:25:09 AM
Creation date
4/6/2022 8:01:22 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0084984
PE
2602
STREET_NUMBER
5800
Direction
E
STREET_NAME
ACAMPO
STREET_TYPE
RD
City
ACAMPO
Zip
95220
APN
01732015
ENTERED_DATE
3/10/2022 12:00:00 AM
SITE_LOCATION
5800 E ACAMPO RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\tsok
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
74
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
for calculating residential flow, developed in consultation with Norman Hantzsche <br />(author of the 1992 paper discussed previously). He indicated that wastewater flow <br />from a single-family residence should be calculated as 100 gallons per day (gpd) for the <br />first bedroom and 50 gpd for each additional bedroom; additional residences should be <br />calculated in the same manner (personal communication, March 4, 2020). <br />Using this method, each three-bedroom home contributes a flow of 200 gpd, for a total <br />estimated flow of 400 gpd. <br />A typical residential concentration of 35 mg/L of nitrate as N was selected for the <br />existing modular home and theoretical residences (Crites and Tchobanoglous, 1998). <br />The estimated flow values discussed here should not be used for the design and sizing <br />of the septic system. The design and sizing of the septic system should utilize the San <br />Joaquin County Environmental Health Department On -Site Wastewater Treatment <br />Systems Standards, which incorporates peak and surge flow factors. The estimates <br />used in the On -Site Wastewater Treatment Systems Standards may be greater than <br />those discussed here. <br />Denitrification Reductions <br />Denitrification is a process that occurs in the septic system drain field whereby certain <br />bacteria oxidize the nitrate (NO3) in the wastewater and release nitrogen gas (N2) to the <br />atmosphere. Due to the biologic processes in the shallow soils, nitrogen in the drain <br />field will may undergo a reduction between 10 percent to 35 percent. Soils with higher <br />clay content, moist soil conditions, high pH, and organic material denitrify by about 35 <br />percent, and soils with high sand content tend to denitrify at a lower rate of about 10 <br />percent. <br />A standard denitrification factor of 25 percent (Hantzsche and Finnemore, 1992) was <br />selected for the Site based on the sandy silt soil present at the percolation test location. <br />Nitrate Loading_ Estimate <br />A nitrate loading scenario was employed to determine the impact from the proposed <br />project to ground water. The scenario utilizes the variables discussed previously, which <br />represent the estimated conditions and uses associated with this project. The following <br />table presents a summary of the assumptions for the nitrate loading calculation for the <br />Site, as presented in Plate 13. <br />LOGE 2212 Page 11 <br />
The URL can be used to link to this page
Your browser does not support the video tag.