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WORK PLANS_2008-2014
Environmental Health - Public
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WORK PLANS_2008-2014
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Last modified
3/31/2020 2:59:40 PM
Creation date
3/31/2020 2:47:46 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
2008-2014
RECORD_ID
PR0506203
PE
2960
FACILITY_ID
FA0007271
FACILITY_NAME
LINCOLN CNTR ENV REMEDIATION TRUST
STREET_NUMBER
0
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
CURRENT_STATUS
01
SITE_LOCATION
PACIFIC AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Geosynte& <br /> consultants <br /> Of the 10 borings to be installed, one boring will be an exploratory boring and nine (9) <br /> borings will be converted into groundwater monitoring wells. The exploratory boring <br /> (EBI on Figure 3) and two (2) monitoring well borings (locations B2 and B4 on <br /> Figure 5) will be advanced to the bottom of the B-zone aquifer, or a maximum of <br /> 140 feet bgs, to collect lithologic data and soil and groundwater chemistry data. Boring <br /> installation activities will be completed in accordance with SOP 1.0 (Appendix B). Soil <br /> sampling techniques are discussed in greater detail below in Section 4.2.1.1. <br /> Once complete, the exploratory boring (EBI) will be destroyed in accordance with <br /> SJEHD requirements. The exploratory boring will be destroyed by backfilling, from the <br /> bottom of the borehole to the surface, with a cement-bentonite grout slurry using a <br /> tremie pipe. Of the remaining nine (9) borings, five (5) will be converted into A-Zone <br /> wells and four (4) will be converted into B-Zone wells as discussed below in Section <br /> 4.2.2. All borings to be converted into monitoring wells shall have a final diameter <br /> equal to the outer diameter of the well casing plus 2-inches on each side. Well <br /> construction details are provided below in Section 4.2.2.1. <br /> 4.2.1.1 Soil Sampling <br /> Soil samples will be collected from differing lithologic layers for both field <br /> classification and laboratory analysis. The field geologist will prepare a log for each <br /> soil boring. Logs will indicate field classification of soils, sampling depths, progress of <br /> drilling, final completion depth, and the nature and resolution of any problems <br /> encountered. The soil core from each boring will be described using the visual-manual <br /> procedures of American Standard for Testing Materials (ASTM) Standard D 2488 for <br /> guidance, which is based on the Unified Soil Classification System (USCS) <br /> (Appendix B, SOP 2.0). <br /> Select soil samples from each boring will be monitored for organic vapors using a <br /> photo-ionization detector (PID). The screening equipment will be calibrated daily <br /> against a span gas (e.g., isobutylene) having a concentration of 100 ppm and recorded <br /> on each log. The soil samples will be monitored by placing a sample of soil retrieved <br /> from the boring into a plastic bag. The soil sample will be broken up in the sealed bag. <br /> The PID probe will then be inserted into the bag to monitor the headspace. <br /> Select soil samples representative of both the A-Zone and B-Zone aquifers will be <br /> collected from the exploratory boring location (location EBI on Figure 3) and the mid- <br /> plume well boring locations (locations B2 and B4 on Figure 5). Each soil sample will <br /> consist of a combined 24 ounces of soil collected from different lithologies <br /> representative of the targeted aquifer zone (i.e. 24 ounces of soil representative of the <br /> Pre-Design Investigation Work Plan 17 18.05.12 <br />
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