My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0010009_SSNL
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
T
>
33 (STATE ROUTE 33)
>
31448
>
2600 - Land Use Program
>
PA-1400037
>
SU0010009_SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
11/20/2024 8:59:19 AM
Creation date
9/9/2019 10:31:11 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0010009
PE
2631
FACILITY_NAME
PA-1400037
STREET_NUMBER
31448
Direction
S
STREET_NAME
STATE ROUTE 33
City
TRACY
Zip
95376-
APN
25531023
ENTERED_DATE
3/31/2014 12:00:00 AM
SITE_LOCATION
31448 S HWY 33
RECEIVED_DATE
3/28/2014 12:00:00 AM
P_LOCATION
98
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\T\HWY 33\31448\PA-1400037\SU0010009\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.
/
69
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
Calculation of Alkalinity Requirement for Nitrification <br /> The nitrate-nitrogen loading calculations are contingent upon the environmental factors required for <br /> nitrification to occur. These conditions include soil pore-space oxygen content, soil temperature, <br /> pH, electrical conductivity, organic matter, cation exchange capacity, and alkalinity. Alkalinity in <br /> wastewater effluent is derived from the on-site well water, in addition to the introduction of wastes <br /> to the effluent stream. Nitrification consumes approximately 7.1 mg of alkalinity for every mg of <br /> ammonia-nitrogen(NH4-N) oxidized. Nitrification of the average Total Nitrogen(TN) <br /> concentration of 60 mg/L, as determined on Page 7, would require: 60 mg/L NH4-N x 7.1 mg <br /> CaCO3 =426 mg/L alkalinity. The alkalinity concentration tested in the well water was 334 mg/L. <br /> Therefore, there is an insufficient alkalinity in the well water for complete nitrification to readily , <br /> proceed without the introduction of wastes. <br /> E. SURFACE WATER INFORMATION <br /> Storm water drainage management will be by on-site retention. Percolating rainwater will <br /> theoretically provide a slight water table dilution effect to percolating wastewater effluent since the <br /> disposal area will be down gradient from the property itself. However, as referenced in the next <br /> Section, rainfall in comparison to evapotranspiration is minimal. <br /> Cym=tic Data: Rainfall versus Evapotranspiration <br /> LS 3.2-.-At is generally and scientifically accepted that when precipitation exceeds <br /> evapotranspiration(Eto), deep percolation of surface rainwater may occur. Evapotranspiration <br /> refers to water evaporation that takes place both at the soil surface and transpiration by plants. <br /> The following Table illustrates rainfall and evapotranspiration for the Tracy area. Precipitation data <br /> was obtained from the Soil Survey of San Joaquin County. The conservative "2 years in 10"data <br /> was used and not the"average rainfall"data. Evapotranspiration data was obtained from the <br /> California Irrigation Management Information System (CIMIS): <br /> TABLE 6 <br /> PRECIPITATION AND Eto DATA FOR TRACY, CA <br /> Month 2 Years in 10 will have more Eto Average Potential Deep <br /> precipitation than: (in/mo) Percolation(in/mo) <br /> (in/mo) (in/day) <br /> January 2.93 1.55 0.05 1.38 <br /> February 2.21 2.24 0.08 -- <br /> March 2.38 3.72 0.12 - <br /> April 1.51 1 5.10 0.17 <br /> May 0.71 6.82 0.22 -- <br /> June 2.09 7.80 0.26 <br /> Page -5- <br />
The URL can be used to link to this page
Your browser does not support the video tag.