My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
FIELD DOCUMENTS
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
C
>
CORRAL HOLLOW
>
1785
>
2900 - Site Mitigation Program
>
PR0517366
>
FIELD DOCUMENTS
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
6/18/2019 5:16:32 PM
Creation date
6/18/2019 4:32:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0517366
PE
2950
FACILITY_ID
FA0013377
FACILITY_NAME
FITZPATRICK HOMES
STREET_NUMBER
1785
Direction
N
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
949412933
CURRENT_STATUS
01
SITE_LOCATION
1785 N CORRAL HOLLOW RD
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\wng
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
190
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
' • �� KLEINFELDER <br /> B-3 GROUNDWATER WELL INSTALLATION <br /> ' B-3.1 Monitorine Well Construction <br /> ' Construction details for shallow groundwater monitoring wells are as follows: <br /> • The well casing are 2- or 4-inch inside diameter, flush threaded joint, schedule 40 PVC <br /> ' pipe. <br /> • The wells are constructed in 8- or 10-inch diameter borings. <br /> ' • Well screen sections are perforated with 0.010- or 0.020-inch factory-cut slots. <br /> ' • The wells are generally screened from 5 feet above to 15 feet below first groundwater. <br /> The screen length is reduced if an aquitard with a minimum thickness of 5 feet is <br /> encountered. If an apparent aquitard is encountered, the well is usually terminated 1 to 2 <br /> ' feet into the aquitard. Effort is made not to screen across two aquifers. If confined <br /> aquifer conditions or high vadose zone contamination are encountered, the well screen is <br /> ' usually not set above the depth of first encountered groundwater. Wells are usually not <br /> set in areas of suspected significant soil contamination. <br /> ' • The PVC pipe and end caps are steam cleaned prior to installation. <br /> • The annular space between the screen and the wall of the boring is backfilled with the <br /> ' appropriate clean sand to approximately 2 feet above the top of the perforated sections. <br /> Based on soil logs or a sieve test, modifications may be made regarding the size of sand <br /> to be used. Installation of the sand may require that the sand be tremmied, using clean <br /> ' water. <br /> • A 3- to 5-foot bentonite plug is placed above the sand pack to provide a seal against <br /> ' surface water infiltration and to reduce the potential for cement grout to infiltrate into the <br /> water. <br /> ' 0 The remaining annular space is filled to the surface with cement/bentonite grout. <br /> • The wells are secured in an aboveground or underground locking stovepipe. The well heads <br /> may be enclosed in a water tight cement utility box set flush to the ground surface when <br /> located in a traffic area. <br /> ' 20-4341-11.E01/201IR959 Page B-4 <br /> Copyright 2001,Mcinfelder,Inc. August 21,2001 <br />
The URL can be used to link to this page
Your browser does not support the video tag.