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Last modified
6/11/2021 10:28:57 AM
Creation date
11/18/2020 2:02:45 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0542459
PE
2965
FACILITY_ID
FA0024400
FACILITY_NAME
CAARNG STOCKTON FMS #24
STREET_NUMBER
8010
Direction
S
STREET_NAME
AIRPORT
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
17726004
CURRENT_STATUS
01
SITE_LOCATION
8010 S AIRPORT WAY
P_LOCATION
01
QC Status
Approved
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EHD - Public
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Soil Boring Results and VEG/ISL ✓orfs Plan <br />Field Maintenance Shop #24, Stockton, California August 2016 <br />utilizing VEG technology. The VEG treatment area is approximately 400 square feet centered <br />around FMS-MW6 (Figure 6) with treatment intervals ranging from 15 to 35 feet bgs. <br />The primary objective of in-situ VEG implementation is to reduce vadose zone source impacts <br />and limit petroleum contaminants from leaching and contributing to groundwater concentrations <br />at the Site. A secondary objective, is to evaluate the effectiveness of in-situ application of VEG <br />technology as a remediation alternative for other ARNG remediation sites. <br />3.2.2. Proposed VEG Scope <br />Prior to any VEG subsurface activities, utility clearances will be performed at the Site to avoid <br />damaging subsurface assets. In addition, an underground service alert (USA) North 811 <br />notification will be made 48 -hours prior any subsurface activities. <br />The VEG treatment area is approximately 400 square feet centered around FMS-MW6 (Figure 6) <br />with treatment intervals ranging from 15 to 35 feet bgs. Prior to the VEG treatment activities, well <br />installation activities will be performed to implement both steam injection and vapor extraction <br />wells within the target area. Injection/extraction wells will be constructed using stainless steel <br />screens and temperature resistant grout. The wells will be installed by a licensed C-57 well <br />contractor. The number of wells and spacing will be determined in the field based on initial radius - <br />of -influence (ROI) testing. The VEG wells will be installed at least two (2) weeks prior to initiation <br />of VEG treatment, allowing for temperature resistant grout to sufficiently cure prior to steam <br />injection. <br />After the installation of the VEG wells, the Remedial Contractor will mobilize all equipment and <br />resources necessary to perform in-situ thermal treatment of petroleum hydrocarbons via VEG in <br />the target treatment area in the vicinity of monitoring well FMS-MW6 (Figure 6). Specifically, <br />treatment across a 20 -foot by 20 -foot surface area centered at FMS-MW6 and along a vertical <br />profile of 15 to 35 feet below ground surface (bgs) is proposed corresponding to an estimated <br />volume of 300 cubic yards. <br />The VEG in-situ treatment is expected to occur over a 2 to 3 -week period, depending on how <br />rapidly the site-specific soils (and inherent soil moisture) thermally respond to the steam injection, <br />as measured by how quickly the temperature of the targeted soils increase by 200 to 300 degrees <br />Fahrenheit (°F) relative to ambient levels. The 2- to 3 -week steam injection activities will be <br />accompanied by approximately one week of soil vapor extraction (i.e., overlapping steam injection <br />and soil vapor extraction during the last week of steam injection). <br />Upon completion of VEG steam injection and treatment activities, the VEG wells will be <br />abandoned. Well abandonment will consist of over-drilling and removal of the top few feet of well <br />casing, followed by grouting in place of the remaining portions of the casings per SJCEHD <br />requirements. <br />3.2.3. VEG Soil Confirmation Sampling <br />Upon completion of well abandonment activities, soil confirmation borings will be advanced within <br />treatment area, allowing for post-treatment soil sampling to take place within the specified vertical <br />profiles subjected to treatment. Up to four (4) soil borings will be advanced in the treatment area <br />and soils will be field screened utilizing a photoionization detector (PID). At a minimum soil <br />samples will be collected at 5 foot intervals from 10 to 35 feet bgs and at locations exhibiting any <br />PID responses greater than 100 parts per million (ppm) from field screening. Soil samples will be <br />submitted to BC Labs for the following analyses: <br />Page 7 <br />
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