My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0005186_SSNL
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
N
>
99 (STATE ROUTE 99)
>
10748
>
2600 - Land Use Program
>
PA-0500401
>
SU0005186_SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
11/19/2024 1:52:16 PM
Creation date
9/8/2019 12:49:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0005186
PE
2611
FACILITY_NAME
PA-0500401
STREET_NUMBER
10748
Direction
N
STREET_NAME
STATE ROUTE 99
City
STOCKTON
APN
08607006 & 07
ENTERED_DATE
7/6/2005 12:00:00 AM
SITE_LOCATION
10748 N HWY 99
RECEIVED_DATE
7/6/2005 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\N\HWY 99\10748\PA-0500401\SU0005186\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.
/
62
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
FFDomestic <br /> WATER FLOW CALCULATIONS AND CHARACTERISTICS <br /> water flows managed by on-site septic systems have been studied for decades with <br /> blished in the scientific literature. Wastewater flows for the Las Palmas project will <br /> "future"basis whereby it will be assumed the existing household will have four <br /> persons per house(husband, wife and two children). <br /> The likelihood of second unit dwellings on any of the subject lots is highly unlikely due to area <br /> constraints, and would be prohibited by EHD due to the nitrate loading calculations for the <br /> subdivision, as illustrated below. If second unit dwellings were allowed,this would push the nitrate <br /> loading projection over the Maximum Contaminant Level (MCL) for drinking water. The total daily <br /> water use is a combination of household and personal uses, as itemized below: <br /> HOUSEHOLD PERSONAL USE <br /> 25 gal for laundry 2 gal for drinking and cooking <br /> 10 gal for dishwashing 3 gal for oral hygiene <br /> 5 gal for misc. use 14 gal for bathing <br /> 16 gal for toilet flushing/sink washing <br /> FLOW RATE in gals/home/day= 40 gals/household/day+(35 gal/person/day x number of persons/home). <br /> The daily wastewater flow rate can be estimated at: <br /> 40 gals+(35 gals x 4 people/home)= 180 gals/day for an average flow per resident of 45 gals. As a safety <br /> factor,the total daily wastewater flow per house and average daily flow per resident will be increased 1.5x to <br /> 270 gals/day and 68 gals/resident,respectively. <br /> The peaking factor for individual residences on septic tanks will vary with the day of the week and <br /> usage. Peak hourly rates are normally associated with the discharge of clothes wash machines, <br /> dishwashers and shower/bath water. The ratio of the peak day to the average day can vary,thus a 1.5 <br /> safety factor. <br /> The characteristics or composition of septic tank effluent is dependent upon several parameters due to <br /> idiosyncrasies within each household. Certain appurtenances change the characteristics of the <br /> wastewater effluent such as filter vaults within septic tanks and kitchen food-waste grinders. <br /> In determining nitrogen concentrations of septic influent and effluent,per capita intake of nitrogen per <br /> day must be estimated. The average American consumes between 70 and 140 g of N/day. Since <br /> nitrogen comprises 16% of the weight of the average protein, 16% of 70 g N= 11 g N/capita/day and <br /> 16%of 140 g N=22 g N/capita/day. The average of these two values is 17 g N/capita/day of <br /> theoretical influent. <br /> The concentration of nitrogen in septic system effluent is normally specified in the scientific literature <br /> as units of mg N/L(milligrams total nitrogen per Liter of effluent). Unfortunately,these units <br /> superimpose wastewater flow variability onto nitrogen influent variability, thus creating even greater <br /> LL—the <br /> ability. One researcher, (Bauman),has averaged the means from 20 other studies to arrive at a <br /> entration of 62 f 21 mg N/L in septic tank effluent. If the above figure for wastewater discharge <br /> timated at 68 gals/resident/day(257 liters) and using the figure of 17 g N/cap/day excreted= 17 g <br /> 7 L=66 mg N/L/day estimated for the proposed Las Palmas project. This concentration will be <br /> stimated nitrogen loading in the effluent discharged from each of the dwellings. <br /> Page -9- <br /> Chesney Consulting <br />
The URL can be used to link to this page
Your browser does not support the video tag.