My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0009004 SSNL
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
V
>
VALPICO
>
12815
>
2600 - Land Use Program
>
PA-1100229
>
SU0009004 SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/7/2020 11:33:48 AM
Creation date
9/9/2019 10:55:03 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0009004
PE
2625
FACILITY_NAME
PA-1100229
STREET_NUMBER
12815
Direction
W
STREET_NAME
VALPICO
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
24008011
ENTERED_DATE
12/19/2011 12:00:00 AM
SITE_LOCATION
12815 W VALPICO RD
RECEIVED_DATE
12/16/2011 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\V\VALPICO\12815\PA-1100229\SU0009004\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.
/
40
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 on Page 8 are contingent upon the environmental factors <br /> required for nitrification to occur. These conditions include soil pore-space oxygen content, soil <br /> temperature, pH, electrical conductivity, organic matter, cation exchange capacity, and alkalinity. <br /> Alkalinity in wastewater effluent is derived from the domestic well water supply in addition to the <br /> introduction of wastes. 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 82 mg/L, as determined on Page 8 would require: 82 mg/L NH4-N x 7.1 mg <br /> CaCO3 = 582 mg/L alkalinity. The alkalinity in the domestic well water supply has yet to be tested <br /> for this project, but it is most likely below this concentration which would thus inhibit nitrification <br /> to an indeterminable degree. <br /> E. SURFACE WATER INFORMATION <br /> Storm water management will consist of an on-site retention basin in the extreme northwest corner <br /> of the property. Percolating stormwater may produce dilution effects to the underlying water table. <br /> Groundwater dilution effects can only be truly discerned with groundwater monitoring and <br /> modeling. According to a scientific paper authored by Shaw and Turyk(1994), reduction of nitrate <br /> concentrations in groundwater can occur primarily through dispersion, or by percolating rainwater, <br /> or a water source including effluent water recharge. <br /> Climatic Data: Rainfall versus Evapotranspiration <br /> S§3 It is generally and scientifically accepted that when precipitation exceeds <br /> spiration(Eto),deep percolation of surface rainwater may"occur. Evapotranspiration <br /> refers to water evaporation that takes place bath atthesoil surface and transpiration by plants. The <br /> following Table illustrates rainfall and evapotranspiration for the Tracy area. Precipitation data was <br /> obtained from the Soil Survey of San Joaquin County. The conservative "2 years in 10"data was <br /> used and not the"average rainfall"data. Evapotranspiration data was obtained from the California <br /> Irrigation Management Information System(CIMIS): <br /> TABLE 4 <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) (in/mo) (in/day) Percolation(in/mo) <br /> January 2.93 1.55 0.05 1.38 <br /> February 2.21 2.24 0.08 -- <br /> March 2.3 8 3.72 0.12 -- <br /> April 1.51 5.10 0.17 <br /> May 0.71 6.82 0.22 -- <br /> June 2.09 7.80 0.26 -- <br /> 5 <br /> Chesney Consulting <br />
The URL can be used to link to this page
Your browser does not support the video tag.