My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SITE INFORMATION AND CORRESPONDENCE_2001-2018
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
N
>
NAVY
>
3515
>
2900 - Site Mitigation Program
>
PR0009241
>
SITE INFORMATION AND CORRESPONDENCE_2001-2018
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/9/2020 8:57:17 AM
Creation date
3/30/2020 1:29:30 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
2001-2018
RECORD_ID
PR0009241
PE
2960
FACILITY_ID
FA0004015
FACILITY_NAME
SHELL OIL (STOCKTON PLANT)
STREET_NUMBER
3515
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
16203002
CURRENT_STATUS
01
SITE_LOCATION
3515 NAVY DR
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
Scanner
SJGOV\wng
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.
/
506
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
Ms. Devra Lewis <br /> February 20, 2003 <br /> Page 2 of 6 <br /> Upon receipt of analytical data from the testing lab, specific locations for additional groundwater <br /> monitoring wells will be identified. Wells will be located in areas outside of the leading edge of <br /> the plume in areas not impacted by petroleum hydrocarbons. Once the locations are determined <br /> and approved, a truck-mounted hollow stem auger (HSA) rig will be mobilized to the site to <br /> install monitor well(s) at specific locationdowngradient of MW-33. Once the new wells are <br /> installed, they will be developed, surveyed, and added to the groundwater monitoring network. <br /> s <br /> A completion report documenting the investigation and well installation activities would then be <br /> provided to the CVRWQCB. The wells would then be sampled at the next scheduled quarterly <br /> event. The following sections discuss the methodologies to be employed during the <br /> investigation. <br /> Proposed Direct Push Locations <br /> Direct push sampling locations have been selected based on recent groundwater plume <br /> information and locations of existing monitoring wells. Approximately 10 direct push sampling <br /> locations will be completed to a depth of approximately 5 feet below the water table. Figure 1 <br /> provides these proposed areas, although exact locations will be determined in the field based on <br /> site conditions and other visual information collected during the geoprobe program. Each soil <br /> core will be logged by a RETEC Field Geologist by ASTM Method D-2488, Standard Practice <br /> for Description and Identification of Soils (Visual-Manual Method). Soils will also be field <br /> screened for volatile constituents with a photoionization detector(PID). <br /> Groundwater Sampling Using Direct Push Methods <br /> Groundwater sampling using direct push methods is discussed briefly in SOP 212, Procedures <br /> for Direct Push Technology Probe System, provided in Appendix A. Additional detail is <br /> provided below. <br /> When using the direct push technology for groundwater sampling, the lead drilling rod section is <br /> fitted with a retractable rod tip, which prevents any solids from entering the sampler. When the <br /> desired depth is reached, the rod is pulled back to expose 3 feet of slotted screen for groundwater <br /> sampling. The procedures for groundwater sampling are as follows: <br /> 1) Position the drill rig at the sampling location <br /> 2) Attach the sampling tool to the end of the drive rods <br /> 3) Advance the rods into the soil, adding sections of blank pipe as necessary <br /> 4) When the desired groundwater sampling depth is reached, unscrew the inner rod <br /> 5) Pull the rod up to expose the screen <br /> 6) Using clean, new polyethylene tubing, pump groundwater from inside the screen. <br /> Purging will be accomplished by lowering the sampling tubing to approximately the <br /> center of the screen and pumping from this location at a rate of 0.1 to 0.5 liters per <br /> minute. A small volume of water will be purged to initiate flow through the screen <br />
The URL can be used to link to this page
Your browser does not support the video tag.