My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0011795 SSNL
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
H
>
HENRY
>
18200
>
2600 - Land Use Program
>
PA-1800114
>
SU0011795 SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/7/2020 11:35:26 AM
Creation date
9/5/2019 11:15:44 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0011795
PE
2622
FACILITY_NAME
PA-1800114
STREET_NUMBER
18200
Direction
S
STREET_NAME
HENRY
STREET_TYPE
RD
City
ESCALON
Zip
95320-
APN
22926027, 22926030
ENTERED_DATE
5/10/2018 12:00:00 AM
SITE_LOCATION
18200 S HENRY RD
RECEIVED_DATE
5/8/2018 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\H\HENRY\18200\PA-1800114\SU0011795\SS 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.
/
36
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
ground surface, followed by partially cemented, silty sand to the full depth of the hole. <br /> The soil logs are presented on Plates 10 through 13. <br /> Discussion of Soil Lithology <br /> Based on the soil observed in the borings, there appears to be limited to moderate <br /> potential for percolation at the test locations. Sandy soils generally have a much <br /> greater potential for percolation than fine-grained or cemented soils. However, a <br /> percolation test is the only accepted method for determining the suitability of the soils <br /> for a septic disposal area. Percolation test results are discussed in the following <br /> section. <br /> Percolation Tests <br /> Shallow percolation tests were conducted on Parcels 1, 2, and 4 of the Site; shallow <br /> and deep percolation tests were conducted on Parcel 3. The soil borings discussed <br /> above were used for the percolation test holes (Plate 9). Percolation test procedures <br /> conformed to San Joaquin County Environmental Health Department policy. <br /> Preparation and Presaturation of Percolation Test Holes <br /> After the borings were advanced by hand auger and the soils logged, the test holes <br /> were completed for the percolation tests. Approximately two inches of pea gravel were <br /> placed in the bottom of each open soil boring, followed by a 2.0-inch diameter PVC pipe <br /> with perforations on the bottom. Pea gravel was then used to backfill a few inches of <br /> the annular space. <br /> Live Oak presaturated the percolation test holes approximately 24 hours prior to the <br /> percolation testing. Each hole was filled with water to a height of 12 inches above the <br /> bottom of the boring for the presaturation. On the day of testing, the holes were found <br /> to be intact and dry. <br /> Percolation Test Procedure <br /> Live Oak conducted the percolation tests for the borings on October 24, 2018. Due to <br /> soil conditions observed, four-hour tests were selected. Water level measurements <br /> were taken every 30 minutes during this four-hour period. The last 30 minutes of each <br /> test were observed by Naseem Ahmed, Registered Environmental Health Specialist at <br /> the San Joaquin County Environmental Health Department. <br /> An electronic well sounder with a depth accuracy of 1/100th foot was utilized for the <br /> water level measurements. The water level was measured against a fixed reference <br /> point on the well casing. Measurements were recorded on the data sheet in decimal <br /> feet. When necessary after measuring the water level, the holes were refilled with water <br /> to a level of six inches or more above the bottom of the hole. <br /> LOGE 1809 Page 5 <br />
The URL can be used to link to this page
Your browser does not support the video tag.