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comprehensive site investigation and remediation objectives report

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BEACON ENVIRONMENTAL SERVICES, INC.<br />

Passive Soil-Gas Survey<br />

Dry Cleaner<br />

Romeoville, IL<br />

flagged in the laboratory <strong>report</strong>. The laboratory method blank analyzed in connection with the<br />

present samples revealed no contamination.<br />

The trip blank is a sampling cartridge prepared, transported, <strong>and</strong> analyzed with other samples but<br />

intentionally not exposed. Any target compounds identified on the trip blanks are <strong>report</strong>ed in the<br />

laboratory data. The analysis of the trip blank (labeled Trip-1 in Table 1) <strong>report</strong>ed none of the<br />

targeted compounds, indicating that the survey <strong>site</strong> itself is the source of detected contamination.<br />

Duplicates. BEACON’s passive soil-gas samplers are prepared with two sets of cartridges for<br />

subsequent duplicate or confirmatory sample analysis. At V3’s request, duplicate analysis was<br />

performed for sample SG-09, designated SG-09 D. Because of finite differences between the<br />

cartridges, <strong>and</strong> the r<strong>and</strong>om nature of diffusive particle movement, comparisons between<br />

duplicates <strong>and</strong> primary samples should be made on a qualitative basis, as quantitative results may<br />

be subject to r<strong>and</strong>om distortions. However, when comparing quantitative results, a duplicate<br />

correspondence should be considered when the relative percent difference (RPD) between the two<br />

samples is less than or equal to 100%. Also, for the purpose of calculating correspondences, all<br />

non-detections should be assigned, as a baseline value, the quantitation level for the specific<br />

contaminant. Based on these assumptions, a 100% correlation was found between the duplicate<br />

sample <strong>and</strong> its base sample.<br />

Survey findings are relative exclusively to this project <strong>and</strong> should not routinely be compared<br />

with results of other BEACON Surveys. To establish a relationship between <strong>report</strong>ed soil-gas<br />

measurements <strong>and</strong> actual subsurface contaminant concentrations, which will indicate those<br />

detections representing significant subsurface contamination, BEACON recommends the<br />

guidelines on the inside front cover of this <strong>report</strong>.<br />

Figures 2-1 <strong>and</strong> 3-1 show the distribution of Tetrachloroethene <strong>and</strong> Total Petroleum<br />

Hydrocarbons (TPH) in the C 5 -C 9 range, respectively, across the entire survey area. Figures 2-2<br />

<strong>and</strong> 3-2 show the distribution of the same compounds, respectively, but focus only on areas<br />

within the survey area, as requested by V3.<br />

The following Attachments are included:<br />

-1- Field Procedures<br />

-2- Field Deployment Report<br />

-3- Laboratory Procedures<br />

-4- Chain-of-Custody Form

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