My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SR0078823 SSNL
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
C
>
CHRISMAN
>
31000
>
2600 - Land Use Program
>
SR0078823 SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
1/15/2020 2:28:37 PM
Creation date
9/4/2019 11:15:23 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0078823
PE
2601
STREET_NUMBER
31000
Direction
S
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25325005,19
ENTERED_DATE
3/7/2018 12:00:00 AM
SITE_LOCATION
31000 S CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\C\CHRISMAN\31000\NL STUDY .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.
/
30
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
TABLE 2 <br /> PERCOLATION TEST RESULTS WITH CORRESPONDING SOIL TYPE, <br /> PERCOLATION RATE AND APPLICATION RATE IN GALLONS/FT2l DAY <br /> jj <br /> 38 INCH DEEP PERC TESD BORING 8.9 min/inch / 0.800 gallons/1'1'/day <br /> LOAM <br /> GROUNDWATER INFORMATION <br /> NLS§2.1. Groundwater depths and elevations throughout San Joaquin County are illustrated on <br /> maps published by the County Flood Control and Water Conservation District. The Fall 2016 <br /> Lines of Equal Depth Maps and the Lines of Equal Elevation Maps indicate groundwater depth and <br /> directional flow. Depth to groundwater is approximately 100 ft below grade and the groundwater <br /> directional flow appears to be in a northeasterly direction. <br /> NLS§ 2.2,3.1. Surrounding agricultural properties are currently farmed and have been for <br /> decades, and surrounding properties have been on septic systems so the potential for nitrate <br /> contamination of the underlying groundwater can be considered significant. <br /> NLS§2.3. The domestic well on the property was sampled and tested for total alkalinity and <br /> nitrate. The alkalinity is low at 138 mg/L and the nitrate concentration is 65 mg/L, 20 mg/L over <br /> the MCL of 45 mg/L. <br /> Discussion on the Alkalinity Requirement for Nitrification <br /> The nitrate-nitrogen loading calculation results 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 well water, in addition to the introduction of <br /> wastes. Nitrification consumes approximately 7.1 mg of alkalinity for every mg of ammonia- <br /> nitrogen(NH4 N) oxidized. Nitrification of the average Total Nitrogen(TN) concentration of 62 <br /> mg/L, as determined below, would require: 62 mg/L NHa N x 7.1 mg CaCO3 =440 mg/L <br /> alkalinity. The alkalinity in groundwater was determined to be 138 mg/L. Therefore, soil <br /> alkalinity and alkalinity from wastes must provide a significant alkalinity concentration for <br /> nitrification to occur. <br /> SURFACE WATER INFORMATION <br /> Climatic Data: Rainfall versus Evapotranspiration <br /> NLS§3.2. It 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 /> Page 3 of 12 <br /> Chesney Consulting <br />
The URL can be used to link to this page
Your browser does not support the video tag.