Final Remedial Action Completion Report for the ... - Rvaap.org
Final Remedial Action Completion Report for the ... - Rvaap.org
Final Remedial Action Completion Report for the ... - Rvaap.org
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<strong>Remedial</strong> <strong>Action</strong> <strong>Completion</strong> <strong>Report</strong><br />
June 2008<br />
Remediation of Soils and Dry Sediments at RVAAP 08-11 (LLs 1-4)<br />
Page 3-4<br />
in<strong>for</strong>mation, each sample container was placed in a sealed plastic bag and <strong>the</strong>n placed in an<br />
ice-filled cooler to ensure preservation.<br />
The submersible pump was lowered slowly until it contacted <strong>the</strong> groundwater surface and <strong>the</strong>n<br />
was continued to be lowered until it reached <strong>the</strong> midpoint of <strong>the</strong> well screen. The pump was<br />
turned on and allowed to operate until a steady flow of groundwater was expelled from <strong>the</strong><br />
Teflon ® return line at <strong>the</strong> ground surface. The discharge line was not allowed to touch any<br />
interior portion of <strong>the</strong> decontaminated sample container or <strong>the</strong> sample matrix within <strong>the</strong><br />
container.<br />
3.2.5 Filtration Procedures<br />
For Shaw groundwater activities, filtered samples were only collected <strong>for</strong> dissolved TAL metals.<br />
Filtration was per<strong>for</strong>med at each well location using a disposable 0.45-micron (µm) pore size<br />
filter assembly and filters were replaced between each well location or as <strong>the</strong>y became restricted<br />
by solids buildup.<br />
3.2.6 Field Quality Control Sampling Procedures<br />
As part of <strong>the</strong> groundwater monitoring activities, Shaw collected three types of quality control<br />
(QC) samples consisting of duplicates, equipment rinsate blanks, and trip blanks in accordance<br />
with Section 4.3.7 of <strong>the</strong> FSAP (SAIC 2001). Duplicate samples of <strong>the</strong> full suite were collected<br />
at a frequency of 10% of <strong>the</strong> field samples collected. This sample frequency applies to matrix<br />
spike/matrix spike duplicate (MS/MSD) samples as well. Equipment rinsate blanks were<br />
collected at a frequency of 10% or, depending on <strong>the</strong> number of samples collected during a day,<br />
one per day per field samples collected at each load line. Temperature and trip blanks consisted<br />
of a sealed container of American Society of Testing and Materials (ASTM) Type I water and<br />
were placed into each cooler used to transport field samples. Trip blanks were analyzed <strong>for</strong><br />
VOC analysis.<br />
3.2.7 Decontamination Procedures<br />
Decontamination of equipment associated with <strong>the</strong> Shaw groundwater sampling activities was<br />
per<strong>for</strong>med in accordance with <strong>the</strong> procedures presented in Section 4.3.8 of <strong>the</strong> FSAP (SAIC<br />
2001).<br />
3.2.8 Summary of Groundwater Sample Results<br />
The purpose of <strong>the</strong> initial groundwater sampling activities was to identify presence of<br />
contaminants in groundwater prior to initiation of Shaw construction activities. Baseline<br />
groundwater sampling was not intended to characterize <strong>the</strong> extent of contamination at <strong>the</strong>se<br />
locations or attempt to ascertain a potential source. However, in order to establish <strong>the</strong> existing<br />
contaminant conditions in groundwater at LLs 1-4, where applicable, results were compared to<br />
<strong>the</strong> United States Environmental Protection Agency (USEPA) Primary Drinking Water<br />
Regulations and <strong>the</strong>ir Maximum Contaminant Limits (MCLs) and Secondary Standards, <strong>the</strong><br />
USEPA Region 9 Preliminary Remediation Goals (PRGs), and <strong>the</strong> RVAAP-established<br />
background criteria and summary statistics (in<strong>org</strong>anics only) <strong>for</strong> bedrock and unconsolidated<br />
zone filtered/unfiltered groundwater background wells. It should be noted that not all <strong>org</strong>anic<br />
and in<strong>org</strong>anic compounds, analyzed as part of <strong>the</strong> baseline groundwater sampling event, have<br />
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