My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0002854 SSNL
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
O
>
OAK
>
8544
>
2600 - Land Use Program
>
SA-97-58
>
SU0002854 SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/7/2020 11:29:30 AM
Creation date
9/8/2019 12:35:44 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002854
PE
2633
FACILITY_NAME
SA-97-58
STREET_NUMBER
8544
Direction
W
STREET_NAME
OAK
STREET_TYPE
ST
City
THORNTON
APN
00119002
ENTERED_DATE
11/1/2001 12:00:00 AM
SITE_LOCATION
8544 W OAK ST
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\O\OAK\8544\SA-97-58\SU0002854\NL_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.
/
48
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
Nue <br /> Our Lady of Sorrows Chapel <br /> Page 6 <br /> poisonings in infants have occurred following the ingestion of water containing nitrate <br /> concentrations greater than 10 mg/1 nitrate as N or 45 mg/1 nitrate as NO3. The units of nitrate in <br /> _ used in the mass balance equation are nitrate-N with a maximum drinking water contaminate <br /> level of 10 mg/l. <br /> The nitrate loading analysis estimates the concentration of nitrate-N of the septic effluent <br /> combined with rain water after denitrification before mixing with ground water. The method is <br /> based on a simple mass balance formula which takes into account soil denitrification, rain fall, <br /> and the proposed waste effluent quantity and nitrate level. Assumptions and calculations for the <br /> analysis are contained on Worksheets No. 1,2,and 3 located in the Appendix. <br /> Denitrification is the biological process in the soil whereby certain bacteria utilize the <br /> oxygen in the nitrate (NOD and release nitrogen gas (N2)to the atmosphere. Denitrification is <br /> expressed as a percentage, and the normally accepted range is 10%to 25%. Sites with higher <br /> clay content,moist soil conditions, and organic material denitrify about 25%or more but sites <br /> with higher sand content and fast peculation rates are estimated to denitrify about 10%. Due to <br /> the lack of fine ma erial in the 20 foot soil column examined, we estimate the denitrification <br /> factor be about'15 %. <br /> In our approach to estimate the nitrate concentration,we used the following variables in <br /> our calculation. <br /> S mmary of Anal sis and Variables Used in the Mass Balance Equation <br /> Result of Denitrification" Deep Rain Waste level' Quantity of Rain Acres <br /> Analysis Percolation discharge Concentration' <br /> (50 people) <br /> 16.49 mg/1 15% 7.86 in/yr 45 mg/1 N 250 gal/day 0.17 mg/l N 0.57 <br /> as N <br /> The results of the analysis indicates that viewing the 0.57-acre site for a period of a year, <br /> the combingd_.rain water and septic effluent after denitrification is estimated to be no greater than <br /> :49 mg/1 as N. this estimate is abo t 1.6 times greater then the maximum contaminate <br /> n ung water standar 10 mg/l as N. Since the use of the building is expected to be much <br /> 4Hantzshe N.N.,Finnemore,E.J. 1991,Predicating Ground-Water Nitrate-Nitrogen Impacts. Ground <br /> Water Vol.30,No.4. <br /> w. <br /> _ <br />
The URL can be used to link to this page
Your browser does not support the video tag.