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SR2400376 (3)
Environmental Health - Public
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2900 - Site Mitigation Program
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SR2400376 (3)
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Entry Properties
Last modified
4/22/2026 1:13:24 PM
Creation date
4/22/2026 12:56:01 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
SR2400376
PE
2900 - Site Mitigation Program
STREET_NUMBER
2000
STREET_NAME
STIMSON
STREET_TYPE
RD
City
STOCKTON
Zip
95206
CURRENT_STATUS
Pending
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
2000 STIMSON RD STOCKTON 95206
Tags
EHD - Public
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Remedial Investigation QAPP <br /> Stockton Army Aviation Support Facility,California <br /> Monitoring wells will be constructed of 2-inch diameter, schedule 40 poly-vinyl chloride (PVC), 10-foot long <br /> 0.01-inch slotted screens, and 10-foot sections of schedule 40 PVC flush threaded riser pipe. A 10 to 20-grade <br /> silica sand filter pack material will then be placed in the annulus between the well pipe and casing. The height <br /> of the filter pack above the top of the screen interval will be 2 feet. As the filter pack is placed in the borehole, <br /> the temporary casing will periodically be vibrated and pulled up, allowing the well materials to settle into the <br /> borehole. If stick-up casings are used, protective bollards will be installed at each corner of the concrete well <br /> pad. Time-release bentonite chips will be placed in the annulus, above the filter pack, and allowed to hydrate. <br /> The bentonite seal will be at least 2 feet thick. The hydration time will be per the recommendations of the <br /> bentonite manufacturer, which is 2 hours for typical types of bentonite chips. Once the bentonite seal has <br /> hydrated, cement-bentonite grout will be placed in the annulus from the top of the bentonite seal up to the <br /> ground surface. Cement-bentonite grout placement will continue until the outer casing is removed from the <br /> borehole. <br /> Monitoring wells will be completed as either flush-mounts using an 8-inch diameter, bolt-down manhole cover <br /> with 12-inch poly skirt or stick-up well casings with manhole/standpipe centered in a 2-foot by 2-foot by 8-inch- <br /> thick concrete pad. The preference of flush-mount or stick-up well casings will be determined based on Facility <br /> preference. <br /> 14.2.6 Soil Sample Collection from Permanent Well Borings <br /> During installation of permanent monitoring wells, borings will be advanced using sonic drilling as described <br /> above in the procedures for Permanent Monitoring Well Installation. All soil cores collected via drilling for well <br /> installation will be logged for Iithological descriptions.Atotal of three soil samples will be collected from each <br /> well location for PFAS analysis: one surface soil sample (0 to 1 ft bgs; collected during the hand clearance <br /> process), one shallow subsurface soil sample from 5 to 6 ft bgs (collected during the hand clearance process), <br /> and one subsurface soil sample approximately 9 to 10 ft bgs. One soil sample (from various depth intervals at <br /> each location) will be analyzed for TOC (USEPA Method 9060A) and pH (USEPA Method 9045D). Geotechnical <br /> soil samples will be collected from the deepest sample intervals at permanent monitoring well locations. Soil <br /> samples will be analyzed under standard turnaround time(TAT)for grain size analysis with sieve and hydrometer <br /> (ASTM D-422), as specified in Worksheets#17 . <br /> Each sample will be collected into laboratory-supplied bottleware and submitted to the laboratory.The laboratory <br /> method DLs for these analytes are presented in Worksheet#15.The required sample containers, preservatives, <br /> and holding times are specified in Worksheets#19. Refer to Parsons SOP PFAS ENV-05:Soil Borings and <br /> Monitoring Well Installation (Appendix D)for additional details. <br /> 14.2.7 Permanent Monitoring Well Development <br /> Permanent monitoring wells will be developed no sooner than 48 hours after completion of well installation when <br /> a cement bentonite grout is used to seal the annular space but shall be developed within seven days of well <br /> installation. Development will be completed by a combination of surging with a surge block, and over-pumping <br /> with a submersible monsoon pump or Waterra pump and associated high-density polyethylene(HDPE)tubing, in <br /> accordance with Parsons SOP PFAS ENV-06:Monitoring Well Development(Appendix D). <br /> Water clarity will be visually monitored and water quality parameters, including dissolved oxygen (DO), specific <br /> conductivity (SC), oxidation reduction potential (ORP), pH, temperature, and turbidity will be measured using a <br /> flow-through cell (per Parsons SOP PFAS ENV-03:Groundwater Sampling)approximately every 5 minutes during <br /> purging to determine progress of development.The water quality meter will be calibrated initially and continually <br /> throughout its usage each day, as needed.A calibration check will be performed at the end of each day. Each <br /> PARSONS Worksheet#14&16: Project Tasks and Schedule <br /> Page 67 <br />
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