My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0002572_SSNL
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
O
>
120 (STATE ROUTE 120)
>
10623
>
2600 - Land Use Program
>
SA-00-33
>
SU0002572_SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
11/19/2024 3:59:58 PM
Creation date
9/8/2019 12:31:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002572
PE
2633
FACILITY_NAME
SA-00-33
STREET_NUMBER
10623
Direction
E
STREET_NAME
STATE ROUTE 120
City
MANTECA
APN
20820025
ENTERED_DATE
10/29/2001 12:00:00 AM
SITE_LOCATION
10623 E HWY 120
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\O\HWY 120\10623\SA-00-33\SU0002572\SS 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.
/
50
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 27, 2000 <br /> Job Number. LG00-312 <br /> Page 8 <br /> balance equation are nitrate-N whose maximum drinking water contaminate level is 10 mg/l. <br /> Denitrification is an important process that mostly occurs in the septic system leach line <br /> whereby certain bacteria utilize the oxygen in the nitrate (NO3) and release nitrogen gas (N2) to <br /> the atmosphere. Denitrification is expressed as a percentage, and the normally accepted range is <br /> 10% to 35%. Soils with higher clay content, moist soil conditions, high pH, and organic material <br /> denitrify about 35% and soils with very high sand content and fast peculation rates are estimated <br /> to denitrify at a lower rate, about 101/6 to 'o. Due to the presence of brown fine to medium <br /> sandy soils, the denitrification factor is estimated to be about 15 %. <br /> In our approach to estimate the quantity of effluent, we used the following information for <br /> our calculation. Fifteen (15) gallons per day per staff/employee and fifteen (15) gallons per day <br /> per student were the estimated use for this type of facility. Since the building is operating 6 hours <br /> per da a fetor of�6/8.was applied to the usage reducing to 11.25 gallons per day per <br /> stafflemployee and student. The average nitrate concentration of the typical septic waste is- <br /> normally consideirA to be. 45 mg/L..-N.6 An adjustment must be added because the ground water <br /> Fwa <br /> nd to contain nitrates at a concentration of 45.6 mg/L-NO3 (10.1 mg/L-N)therefore a <br /> f 55.1 mg/1-N was used (45 +_10.1 = 55.1 mg/L-N, estimated level of wasi' 'stream). <br /> The amount of students and staff that the site could occupy the site without exceeding the <br /> or Nitrate was determined to be twenty-five (25) students and eight (8) staff/employees <br /> e present septic system. Several trial runs were performed using thirty-six (36) students <br /> er the MCL for nitrates was exceeded. The analysis indicated that a maximum of twenty- <br /> 5) students and eight (8) staff/employees could occupy the facility with respect to nitrate <br /> using the a typical, non-engineered septic system. The following tables present the input <br /> d results of the nitrate loading analysis. A result under 10 mg/L-N (the MCL for drinking <br /> is considered acceptable. <br /> 6 U.S.Environmental Protection Agency(EPA). 1980. Design Manual: On-Site Wastewater Treatment <br /> and Disposal Systems. Report No. EPA-625/ 1-80-012. 390 pp. <br /> pEts�y <br /> F <br />
The URL can be used to link to this page
Your browser does not support the video tag.