My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS XR0001802
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
C
>
CHEROKEE
>
225
>
2900 - Site Mitigation Program
>
PR0508009
>
ARCHIVED REPORTS XR0001802
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/20/2019 2:26:53 PM
Creation date
5/20/2019 2:06:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001802
RECORD_ID
PR0508009
PE
2957
FACILITY_ID
FA0007882
FACILITY_NAME
ARCO #760
STREET_NUMBER
225
Direction
S
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04314058
CURRENT_STATUS
01
SITE_LOCATION
225 S CHEROKEE LN
P_LOCATION
02
P_DISTRICT
004
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.
/
21
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
December 8, 1993 Working to Restore Nature <br /> ARCO Station No 760, Lodi, California <br /> The annular space in the well is packed with sand compatible with well slot size to <br /> approximately 1 to 2 feet above the slotted interval A 3-foot thick bentonite plug is added <br /> above the sand pack to prevent the cement from entering the well pack The remaining <br /> annulus is backfilled to grade with a bentonite cement slurry <br /> Wells are protected with a traffic-rated, cast-aluminum utility box equipped with a PVC <br /> skirt The box has a watertight seal to protect against surface-water infiltration and must <br /> be opened with a special wrench. The design of this box discourages vandalism and reduces <br /> the possibility of accidental disturbance of the well <br /> Well Development <br /> We wait a minimum of 24 hours after well installation before developing the groundwater <br /> monitoring wells to allow the grout to seal Before developing the monitoring wells, a water <br /> sample is collected for subjective analysis from near the water surface in the well with a <br /> Teflon bailer cleaned with a laboratory-grade detergent and deionized water The wells are <br /> developed with a surge block and pump Well development continues until the discharge <br /> water is clear of silt and sand Clay-size sediments derived from the screened portion of the <br /> formation cannot be entirely eliminated by well development After the wells stabilize for <br /> a minimum of 24 hours, the wells are purged of stagnant water and a sample is collected <br /> for laboratory analysis See the section on groundwater sampling <br /> Subjective Analysis of Q <br /> iroundwater Samples <br /> Groundwater samples are collected for subjective analysis from dust below the air-fluid <br /> interface in a monitoring well by lowering approximately half the length of a clean Teflon <br /> bailer through the interface The bailer is retrieved and the water sample examined for <br /> floating product, sheen, or other subjective evidence of hydrocarbons <br /> Measurement of the Depth to Groundwater in Monitoring Wells <br /> The depth of the groundwater surface in a monitoring well is measured from the top of the <br /> well casing to the nearest 0 01 foot with a Solinst or similar electric water-level indicator _ <br /> The well will be vented to the atmosphere before obtaining depth-to-water measurements <br /> Venting is conducted to allow the groundwater to equilibrate to barometric pressure These <br /> measurements will be combined to evaluate the elevation of the groundwater surface in each <br /> well and the slope of the groundwater surface across the <br /> site. <br /> 0913ccar <br /> 38048-10 <br />
The URL can be used to link to this page
Your browser does not support the video tag.