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SWMU Oxidation Pond (O-1)
Table 2 - Shallow Soil Boring Analytical Results, November 1999
Sample ID | O1-SB10e | O1-SB11 | O1-SB12e | O1-SB13e | O1-SB14 | O1-SB101d,e | O1-SB15e | O1-SB16e | O1-SB17e | O1-SB18f | O1-SB19 | O1-SB20e | O1-SB102d,e | |||||||||||||||||||
Depth (ft) | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | |||||||||||||||||||
Soil Type | Tarrant | Tarrant | Tarrant | Tarrant | Tarrant | Tarrant | Tarrant | Tarrant | Tarrant | Tarrant | Tarrant | Tarrant | Tarrant | |||||||||||||||||||
Date Collected | 11/7/99 | 11/7/99 | 11/7/99 | 11/7/99 | 11/8/99 | 11/8/99 | 11/8/99 | 11/8/99 | 11/8/99 | 11/8/99 | 11/8/99 | 11/8/99 | 11/8/99 | |||||||||||||||||||
| Comparison Criteria | Sample Analytical Results | ||||||||||||||||||||||||||||||
Constituent | Lab MDLa | Lab RL | Back-groundb Tarrant | RRS2-GWPc | RRS2-SAIc | |||||||||||||||||||||||||||
VOCs, SW8260B (mg/kg): | ||||||||||||||||||||||||||||||||
Tetrachloroethene | 0.00016 | 0.007 | -- | 0.5 | 17 | 0.003 | R* | 0.00016 | M | 0.0006 | R* | 0.023 | R* | 0.0377 | M | 0.00016 | R* | 0.00016 | R* | 0.00016 | R* | 0.00016 | R* | 0.00016 | R* | 0.00016 | M | 0.00016 | R* | 0.00016 | R* | |
cis-1,2-Dichloroethene | 0.00021 | 0.006 | -- | 7 | 20,000 | 0.00021 | M | 0.00021 | M | 0.00021 | R* | 0.0007 | R* | 0.00021 | M | 0.00021 | R* | 0.00021 | R* | 0.00021 | R* | 0.00021 | R* | 0.00021 | R* | 0.00021 | M | 0.00021 | R* | 0.00021 | R* | |
trans-1,2-Dichloroethene | 0.00024 | 0.003 | -- | 10 | 41,000 | 0.00024 | U | 0.00024 | U | 0.00024 | R* | 0.00024 | R* | 0.00024 | U | 0.00024 | R* | 0.00024 | R* | 0.00024 | R* | 0.00024 | R* | 0.00024 | R* | 0.00024 | U | 0.00024 | R* | 0.00024 | R* | |
Trichloroethene | 0.0002 | 0.01 | -- | 0.5 | 6.6 | 0.0002 | M | 0.0002 | M | 0.0002 | R* | 0.003 | R* | 0.0002 | M | 0.0002 | R* | 0.0002 | R* | 0.0002 | R* | 0.0002 | R* | 0.0002 | R* | 0.0002 | M | 0.0002 | R* | 0.0002 | R* | |
Vinyl Chloride | 0.00026 | 0.009 | -- | 0.2 | 0.007 | 0.00026 | M | 0.00026 | M | 0.00026 | R* | 0.00026 | R* | 0.00026 | M | 0.00026 | R* | 0.00026 | R* | 0.00026 | R* | 0.00026 | R* | 0.00026 | R* | 0.00026 | M | 0.00026 | R* | 0.00026 | R* | |
Toluene | 0.0015 | 0.005 | -- | 100 | 2,400 | 0.0042 | F | 0.0016 | F | 0.0056 | R* | 0.0069 | R* | 0.0053 | 0.00015 | R* | 0.00015 | R* | 0.00015 | R* | 0.00015 | R* | 0.00015 | R* | 0.00015 | U | 0.00015 | R* | 0.0093 | R* | ||
m,p-Xylenes | 0.00022 | 0.007 | -- | 1,000 | 3,300 | 0.0011 | R* | 0.00022 | U | 0.0007 | R* | 0.0006 | R* | 0.00022 | U | 0.00022 | R* | 0.00022 | R* | 0.00022 | R* | 0.00022 | R* | 0.00022 | R* | 0.00022 | U | 0.00022 | R* | 0.00022 | R* | |
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Total Metals (mg/kg): | ||||||||||||||||||||||||||||||||
Cadmium, SW7131A | 0.022 | 0.1 | 0.45 | 0.50 | 1,000 | 0.15 | M | 0.03 | M | 0.09 | M | 0.03 | M | 0.06 | M | 0.07 | M | 0.02 | M | 0.06 | M | 0.09 | M | 0.13 | M | 0.06 | M | 0.06 | M | 0.06 | M | |
Chromium, SW6010A | 0.08 | 20 | 39.9 | 10 | 240,000 | 19.3 | M | 7.0 | M | 5.4 | M | 13.5 | M | 13.8 | M | 12.1 | M | 15.7 | M | 13.4 | M | 14.0 | M | 61.2 | M | 22.4 | M | 7.5 | M | 7.0 | M | |
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Solids (%): | -- | -- | -- | -- | -- | -- | 87.7% | 95.2% | 93.5% | 93.8% | 94.1% | 94.5% | 93.9% | 90.0% | 92.2% | 89.0% | 95.8% | 91.2% | 90.2% | |||||||||||||
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Sample ID | O1-SB21 | O1-SB22e | O1-SB23 | O1-SB24 | ||||||||||||||||||||||||||||
Depth (ft) | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | 0 - 4.0 | ||||||||||||||||||||||||||||
Soil Type | Tarrant | Tarrant | Tarrant | Tarrant | ||||||||||||||||||||||||||||
Date Collected | 11/8/99 | 11/8/99 | 11/8/99 | 11/8/99 | ||||||||||||||||||||||||||||
Constituent | ||||||||||||||||||||||||||||||||
VOCs, SW8260B (mg/kg): | ||||||||||||||||||||||||||||||||
Tetrachloroethene | 0.00016 | M | 0.00016 | R* | 0.0146 | M | 0.00016 | M | ||||||||||||||||||||||||
cis-1,2-Dichloroethene | 0.00021 | M | 0.00021 | R* | 0.00021 | M | 0.00021 | M | ||||||||||||||||||||||||
trans-1,2-Dichloroethene | 0.0031 | 0.00024 | R* | 0.00024 | U | 0.00024 | U | |||||||||||||||||||||||||
Trichloroethene | 0.0002 | M | 0.0002 | R* | 0.0002 | M | 0.015 | M | ||||||||||||||||||||||||
Vinyl Chloride | 0.00026 | M | 0.00026 | R* | 0.00026 | M | 0.00026 | M | ||||||||||||||||||||||||
Toluene | 0.00015 | U | 0.00015 | R* | 0.0051 | 0.00015 | U | |||||||||||||||||||||||||
m,p-Xylenes | 0.00022 | U | 0.00022 | R* | 0.00022 | U | 0.00022 | U | ||||||||||||||||||||||||
Total Metals (mg/kg): | ||||||||||||||||||||||||||||||||
Cadmium, SW7131A | 0.04 | M | 0.03 | M | 0.11 | M | 0.022 | M | ||||||||||||||||||||||||
Chromium, SW6010A | 12.3 | M | 11.2 | M | 57.1 | M | 8.7 | M | ||||||||||||||||||||||||
Solids (%): | 87.7% | 95.8% | 84.4% | 92.2% | ||||||||||||||||||||||||||||
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Notes: All samples analyzed by O'Brien & Gere Laboratory, Syracuse, New York. a MDLs were not adjusted for moisture content. b Background values from Evaluation of Background Metals Concentrations in Soil Types at Camp Stanley Storage Activity, June 1996. c Industrial risk reduction standards for groundwater protection and soil-air ingestion. d Duplicate sample. e Sample was reanalyzed, and all analyte results were rejected in the reanalysis. f Sample was reanalyzed and analyte results were from the reanalysis. | ||||||||||||||||||||||||||||||||
Concentrations exceeding RRS1 background levels are in bold type. | ||||||||||||||||||||||||||||||||
Concentrations exceeding RRS2 standards are highlighted. | ||||||||||||||||||||||||||||||||
* Due to the high alkalinity of the soil, Parsons ES is requesting to use this data. | ||||||||||||||||||||||||||||||||
AFCEE QAPP 3.0 Data Qualifiers: U The analyte was analyzed for, but not detected. The associated numerical value is at or below the MDL. F The analyte was positively identified but the associated numerical value is below the RL. M A matrix effect was present. R The data are unusable due to deficiencies in the ability to analyze the sample and meet QC criteria. J The analyte was positively identified, the quantitation is an estimation. |