My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0006024 SSNL
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
M
>
MACARTHUR
>
24500
>
2600 - Land Use Program
>
PA-0500776
>
SU0006024 SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/7/2020 11:32:02 AM
Creation date
9/6/2019 9:54:54 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0006024
PE
2656
FACILITY_NAME
PA-0500776
STREET_NUMBER
24500
Direction
S
STREET_NAME
MACARTHUR
STREET_TYPE
DR
City
TRACY
APN
25024001
ENTERED_DATE
5/5/2006 12:00:00 AM
SITE_LOCATION
24500 S MACARTHUR DR
RECEIVED_DATE
5/3/2006 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\M\MACARTHUR\24500\PA-0500776\SU0006024\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.
/
106
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
Assigning the following parameters to be averaged to provide the ADF: 1.) 15 gallons per person <br /> who Assigning <br /> be parked in the total number of parking stalls, 2.) 150 gpd for each toilet, and 3.)A <br /> reasonable number of maximum toilet flushes: <br /> O 96 parking stalls x 15 gals assigned to one person parked in one stall= 1,440 gallons per day(gpd) <br /> ® 22 toilets x 150 gallons per toilet per day=3,300 gpd <br /> OO 6 flushes/hr/toilet x 22 toilets x 8 hrs/day= 1,056 flushes/day x 1.5 gals/flush= 1,584 gpd <br /> Average= 1,440+3,300 + 1,584=6,324=3 =2,108 gpd ADF <br /> COMMERCIAL WASTEWATER CHARACTERISTICS <br /> Primary wastewater constituents-of-concern found in septic tank effluent have influence over two <br /> important factors in the operation of an on-site wastewater disposal system: Soil effluent <br /> acceptance rates and nitrate-nitrogen impact. The Biochemical Oxygen Demand(BOD) test is the <br /> most common test used in wastewater analysis, but can be unreliable for determining organic <br /> matter in water. BOD is the amount of oxygen, expressed as mg/L or ppm, that bacteria take from <br /> water when they oxidize organic matter. To determine BOD, oxygen the bacteria uses is calculated <br /> by comparing the amount left at the end of 5 days with the known amount at the beginning. <br /> Adsorption and volatilization, followed by microbial degradation are the primary processes for <br /> removal of soluble organics. <br /> Total Suspended Solids (TSS) is the material retained on a standard glass-fiber filter disk. <br /> Suspended solids can be categorized as volatile or fixed suspended solids. TSS can create and <br /> enhance the biomat formation between the soil and effluent interface, thus restricting infiltration. <br /> The biomat, also referred to as a"clogging mat," is a biological, slimy substance which forms on <br /> the soil-effluent interface over time. This mat is composed mostly of aerobic and anaerobic <br /> bacteria and bacterial products consisting of polyuronides and polysaccharides. The biomat does <br /> have one beneficial property and that is removing approximately 10% of the nitrogen from gravity <br /> flow disposal systems. It is unknown how much, if any,biomat material forms under pressurized <br /> filter bed systems. Consequently, this 10%nitrogen removal figure will not be used in the nitrate <br /> loading calculations on Page 14 to reduce the calculated nitrate loading. <br /> Total Nitrogen is the summation of ammonia-nitrogen (NH4) and organic nitrogen(proteins, amino <br /> acids, enzymes). Since the septic tank is predominately anaerobic, nitrogen cannot exist in its <br /> oxidized state as nitrate for any length of time in the septic tank effluent, and if it does, it is quickly <br /> reduced to NO or NOZ. If nitrate existed in septic tank effluent, this would also be added to <br /> ammonium and organic nitrogen to arrive at Total Nitrogen. Although there is a restroom on the <br /> existing premises that serves the Tracy Cold Storage business, the septic tank could not be located <br /> to obtain a representative septic tank effluent sample. <br /> NLS§3.3 A sample from the on-site septic tank may not have been truly representative of a <br /> commercial system because of the low number of people who use, and have used, this septic <br /> system. Consequently, to quantify the anticipated nitrogen concentration for use in the nitrate <br /> loading calculations from the built-out Ice House project, effluent sample test results were obtained <br /> from another commercial facility in the Tracy area. These analytical test results (three total tests) <br /> were averaged to provide the concentrations found in Column 2, in Table 5 below. <br /> 12 <br /> Chesney Consulting <br />
The URL can be used to link to this page
Your browser does not support the video tag.