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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 |
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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 |
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Soil Type |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
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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 |
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|
Comparison Criteria |
Sample Analytical Results |
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Constituent |
Lab MDLa |
Lab RL |
Back-groundb Tarrant |
RRS2-GWPc |
RRS2-SAIc |
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VOCs, SW8260B (mg/kg): |
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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* |
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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): |
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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 |
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Depth (ft) |
0 - 4.0 |
0 - 4.0 |
0 - 4.0 |
0 - 4.0 |
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Soil Type |
Tarrant |
Tarrant |
Tarrant |
Tarrant |
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Date Collected |
11/8/99 |
11/8/99 |
11/8/99 |
11/8/99 |
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Constituent |
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VOCs, SW8260B (mg/kg): |
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Tetrachloroethene |
0.00016 |
M |
0.00016 |
R* |
0.0146 |
M |
0.00016 |
M |
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cis-1,2-Dichloroethene |
0.00021 |
M |
0.00021 |
R* |
0.00021 |
M |
0.00021 |
M |
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trans-1,2-Dichloroethene |
0.0031 |
0.00024 |
R* |
0.00024 |
U |
0.00024 |
U |
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Trichloroethene |
0.0002 |
M |
0.0002 |
R* |
0.0002 |
M |
0.015 |
M |
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Vinyl Chloride |
0.00026 |
M |
0.00026 |
R* |
0.00026 |
M |
0.00026 |
M |
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Toluene |
0.00015 |
U |
0.00015 |
R* |
0.0051 |
0.00015 |
U |
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m,p-Xylenes |
0.00022 |
U |
0.00022 |
R* |
0.00022 |
U |
0.00022 |
U |
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Total Metals (mg/kg): |
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Cadmium, SW7131A |
0.04 |
M |
0.03 |
M |
0.11 |
M |
0.022 |
M |
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Chromium, SW6010A |
12.3 |
M |
11.2 |
M |
57.1 |
M |
8.7 |
M |
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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. |
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Concentrations exceeding RRS1 background levels are in bold type. |
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Concentrations exceeding RRS2 standards are highlighted. |
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* Due to the high alkalinity of the soil, Parsons ES is requesting to use this data. |
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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. |