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SR0084222 (2)
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SR0084222 (2)
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Last modified
10/18/2022 11:53:00 AM
Creation date
10/18/2022 11:50:22 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
SR0084222
PE
2903
FACILITY_ID
FA0006725
FACILITY_NAME
NAVAL COMPUTER AND TELECOMMUNICATION STATION, FORMER (NCTS)
STREET_NUMBER
1200
STREET_NAME
HUMPHREYS
City
STOCKTON
Zip
95203
APN
16203007
ENTERED_DATE
9/16/2021 12:00:00 AM
SITE_LOCATION
1200 HUMPHREYS
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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Work Plan, PFAS Site Inspection <br />Naval Computer and Telecommunications Station Stockton, California Technical Approach <br /> 3-5 DCN: TRBW-0202-5183-0010 <br />Appendix A). After collection, the samples will be placed in a cooler, chilled with ice, and shipped <br />under chain-of-custody protocol to SGS Laboratories for PFAS analysis. Approximately 25% of <br />the soil samples will be analyzed for TOC. <br />Once complete, borings will be tremie grouted from the bottom to the surface with a portland <br />cement/5 percent (%) bentonite mix. All decontamination water and drill cuttings will be <br />containerized for IDW management according to the Waste Management Plan (Section 4). The <br />total number of soil analysis samples for each analyte group is tabulated in Worksheet #18 and <br />detailed in Worksheet #17 of the SAP. Worksheet #19 in the SAP presents a summary of the <br />sample analysis, container types and volumes, preservation requirements, and holding times for <br />the soil, sediment, groundwater, and IDW samples collected. <br />3.4.2 Direct Push Groundwater Sampling <br />Groundwater samples will be collected from select direct push boring locations of each AOC. The <br />rationale for sample locations is presented in Worksheet #17 of the SAP and samples will be <br />labeled by field personnel as they are collected. The groundwater samples will be collected by <br />installing 5 to 10 feet of three-quarter-inch polyvinyl chloride (PVC) screen connected to a riser <br />pipe inside the direct push casing and pulling back the casing to expose the screen. If site conditions <br />allow, a well volume may be purged prior to collecting a groundwater sample. A groundwater grab <br />sample will be collected using temporary well procedures in accordance with SOP -009 <br />(Attachment 1 in Appendix A). Groundwater samples will be logged on the Groundwater Sample <br />Collection Field Sheet (Attachment 1 in Appendix A). The groundwater samples will be analyzed <br />for PFAS compounds. Once sampling is complete, borings will be tremie grouted from the bottom <br />to the surface with a portland cement/5% bentonite mix. All purge water and decontamination <br />water will be containerized for IDW management according to the Waste Management Plan <br />(Section 4). <br />Before collection of groundwater samples, the depth of the static groundwater level will be <br />measured in the groundwater monitoring wells using an electronic water level meter to evaluate <br />groundwater flow direction. The depth will be measured in units of feet (to the nearest 0.01 foot) <br />with respect to the top of each well casing, to determine the depth to water below ground surface. <br />Water levels will be recorded on the Groundwater Sample Collection Field Sheet. The water level <br />meter will be decontaminated prior to use and between each monitoring well. <br />3.4.3 Groundwater Quality Monitoring and Groundwater Sampling <br />Groundwater monitoring wells will be purged using low-flow purging methods via a peristaltic <br />pump prior to sample collection. The water level and total depth of each well will be measured <br />before the start of purging. Measurements of pH, specific conductance, turbidity, temperatur e, <br />oxidation-reduction potential, and dissolved oxygen will be made during purging and recorded on <br />the Groundwater Sample Collection Field Sheet. If stabilization cannot be achieved after 30
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