Environmental Engineering Reference
In-Depth Information
TABLE 10.10
CRF SOIL Values for Select PAHs
PAH Compound
Soil Type
CRF SOIL
Naphthalene
Clay
11.8
Silty clay
1.24
Sand silty clay
1.06
Sand
0.37
Chrysene
Clay
2,407.00
Silty clay
240.00
Sand silty clay
204.00
Sand
61.00
Benzo[b]fluoranthrene
Clay
146.00
Silty clay
14.60
Sand silty clay
12.40
Sand
3.70
Benzo[k]fluoranthrene
Clay
126.00
Silty clay
12.60
Sand silty clay
10.70
Sand
3.21
Phenanthrene
Clay
70.00
Silty clay
7.00
Sand silty clay
5.90
Sand
1.80
Benzo[g,h,i] perylene
Clay
1,080.00
Silty clay
108.00
Sand silty clay
91.00
Sand
27.50
Benzo(a)pyrene
Clay
797.30
Silty clay
79.70
Sand silty clay
67.50
Sand
20.20
Mean PAH CRF SOIL
Clay
662.58
Silty clay
66.16
Sand silty clay
55.23
Sand
16.82
Source:
Kaufman, M.M. et al., Environ. Geol ., 56,
1009, 2009.
highest likelihood of contaminating groundwater, whereas the low mean ratios of PCBs,
mercury, and chlordane position them as posing the greatest contamination threat to soil.
This conclusion is supported by the average extents of contamination shown in column 6,
which were measured using analytical data from hundreds of sites (Kaufman et al. 2005,
Rogers et al. 2007a; Kaufman et al. 2009). The measured extents of contamination listed
in the rightmost column represent contaminants at concentrations exceeding the appli-
cable regulatory action level from an identified anthropogenic source. As predicted by the
computed CRF GW /CRF SOIL ratios, the average extents of contamination were the largest for
chromium VI and DNAPL compounds.
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