My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_XR0012662
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
W
>
WILSON
>
1100
>
2900 - Site Mitigation Program
>
PR0507217
>
ARCHIVED REPORTS_XR0012662
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
6/23/2020 5:14:51 PM
Creation date
6/23/2020 2:16:15 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012662
RECORD_ID
PR0507217
PE
2950
FACILITY_ID
FA0007741
FACILITY_NAME
AUTO ZONE INC
STREET_NUMBER
1100
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95202
APN
11733035
CURRENT_STATUS
02
SITE_LOCATION
1100 N WILSON WAY
P_LOCATION
01
QC Status
Approved
Scanner
LSauers
Tags
EHD - Public
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
450
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
ME <br /> Offl EVA <br /> Coca-Cola EnterprisQ,, - West <br /> Job No. 9GO54 <br /> Soil gas surveys consist of the sampling and analysis of the soil gases that reside in the <br /> pore space of the wtsaturated zone above the water table. Since many of the common <br /> organic compound:, and industrial solvents exhibit significant .;vapor pressures and are <br /> relatively insoluble in water, their introduction into subsurface soils results in vapor phase <br /> perr._�ation and transport. Should these chemicals reach the water table and travel with the <br /> groundwater, vapors will continue to emanate from the contaminated groundwater into <br /> overlying soils. Thus, organic contamination of the subsurface soils or groundwater can be <br /> detected by measuring the relative concentration of volatile organics in the soil gas. <br /> Sampling locations for the soil gas survey were selected by superimposing an imaginary 20- <br /> foot grid over the existing tank area. The expected groundwater flow is to the southwest. <br /> Sample points were selected to encompass any groundwater flow in and around the old tank <br /> excavation, therefore locations were weighted heavily in the downgradient direction (Figure <br /> 2). Also, as analytical data were received, additional sampling locations were added to <br /> estimate the outer Iimits of the contamination plume. <br /> Soil gas samples were collected with a sampling probe consisting of 3/4-inch galvanized <br /> pipe tipped with a reusable aluminum point. A probe was driven inti the ground at each <br /> sampling Iocation to a depth of 5 to 13 feet below Iand surface using aTruck-mounted, <br /> hydraulically-actuated point driver. The probe was then pulled up 6 inches to expose the <br /> sampling interval. A regulated vacuum pump was attached to the probe with a teflon tube <br /> adaptor. A minimum of 2 to 5 liters of soil gas were purged to ensure that a representative <br /> soil gas sample would be collected. The samples were collected by withdrawing the soil gas <br /> T from a short piece of connecting silicon rubber tube using a calibrated glass syringe. <br /> Duplicate samples in volumes ranging from 1 ml to 2 ml, depending on the VOC <br /> W concentration, were also collected. All holes left in the ground or pavement surface from the <br /> soil gas point removal were filled with neat cement. <br /> 3 <br />
The URL can be used to link to this page
Your browser does not support the video tag.