My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
WORK PLANS
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
R
>
ROTH
>
700
>
2900 - Site Mitigation Program
>
PR0542675
>
WORK PLANS
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/17/2026 10:41:30 AM
Creation date
3/11/2025 2:50:43 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0542675
PE
2954 - USEPA - SITE PROJECT
FACILITY_ID
FA0024553
FACILITY_NAME
SHARPE ARMY DEPOT
STREET_NUMBER
700
STREET_NAME
ROTH
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19802001
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
700 ROTH RD LATHROP 95330
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.
/
395
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
Soil Sampling Field Standard Operating Procedure <br /> SWE-FSOP-405;Revision 1 Ahtna Southwest Environmental Operations <br /> 9. Make notes on the boring log regarding the soil characterization and geologic features, including any <br /> staining or odors (ensure no inhalation hazard exists). See SWE-FSOP-201 (Soil Classification). Note <br /> that samples should generally be collected before the characterization of soil to preserve the <br /> integrity of the volatile samples. <br /> 10. Wipe down the jar threads to remove any bits of soil and close the jar with the lid, and wipe the <br /> outside of the jar using a paper towel or other clean, dry wipes. <br /> 11. Label the sample container with the appropriate information;typically, use a label with waterproof <br /> adhesive, or if not, secure the label with clear tape. <br /> 12. Place the sample container in the shipping container,typically a chilled cooler, and proceed with <br /> further sampling. <br /> 13. When sampling is complete, all reusable downhole/sampling equipment and any drill rig <br /> components that may have come in contact with contaminated soil should be decontaminated <br /> before next use. <br /> For specific types of sampling, follow the steps outlined in the following sections. <br /> 4.3.1 Discrete Sampling <br /> Typically, discrete sampling is used unless otherwise dictated for the specific project.The locations and <br /> depths where discrete samples are collected should be explained in a site-specific work plan. <br /> 4.3.2 Composite Sampling <br /> Composite sampling may only be conducted if previously approved in a site-specific work plan. If <br /> possible, coordinate with the testing laboratory if laboratory composting is possible. <br /> Composite samples should have equal aliquots of soil collected as discrete samples from all sub- <br /> locations. If composite samples are necessary, aliquots of volatile samples are collected directly into <br /> laboratory-supplied jars and preserved immediately according to directions from the laboratory. <br /> Aliquots of non-volatile samples should be homogenized before placing into laboratory-supplied jars. <br /> 4.3.3 Incremental Sampling Methodology <br /> ISM sampling may only be conducted if previously approved in a site-specific work plan.The method <br /> uses primary, replicate, and triplicate samples of the decision unit collected from many(30-50) sub- <br /> samples (aliquots) to create a statistically valid result. See SWE-FSOP-407 (Soil Incremental Sampling <br /> Methodology).The ISM sampling approach shall be conducted following the Interstate Technology& <br /> Regulatory Council (ITRC) Incremental Sampling Methodology Guidance (ITRC, 2012). <br /> ISM sampling is similar to a composite sample in that equal aliquots of soil are collected in each gridded <br /> or celled decision unit (grid/cell dimensions to be determined based on decision unit size), using a <br /> random number generator to establish random planer and depth coordinates. A duplicate and triplicate <br /> sample should be collected using the same techniques as the primary sample to verify that the ISM <br /> sample truly represents the decision unit. Care should be taken to ensure triplicate samples are not <br /> collected from co-located or adjacent locations. <br /> Page 12 of 15 <br />
The URL can be used to link to this page
Your browser does not support the video tag.