Table 5. Concentrations of selected polycyclic aromatic hydrocarbons measured by semipermeable membrane devices (SPMDs) at three sites in the McKenzie River basin, Oregon, September–October 2007.
[A and B are replicate samples. MDL, method detection limit; MQL, method quantitation limit; “<,” compound not present at MDL; NQ, not quantified--compound detected at a level less than the MQL; detections are highlighted as bold type in shaded cells]
| Polycyclic aromatic hydrocarbons |
Concentrations, in nanograms of chemical per deployed SPMD |
| Water-treatment plant inlet |
|
Cedar Creek |
|
Camp Creek |
MDL |
MQL |
| A |
B |
A |
B |
A |
B |
| Naphthalene |
<50 |
<50 |
|
<50 |
<50 |
|
<50 |
<50 |
50 |
88 |
| Acenaphthylene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| Acenaphthene |
<26 |
<26 |
|
<26 |
<26 |
|
<26 |
<26 |
26 |
78 |
| Fluorene |
<2 |
<2 |
|
NQ |
10 |
|
10 |
10 |
2 |
10 |
| Phenanthrene |
<23 |
NQ |
|
NQ |
NQ |
|
NQ |
NQ |
23 |
49 |
| Anthracene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| Fluoranthene |
<13 |
NQ |
|
NQ |
NQ |
|
NQ |
NQ |
13 |
39 |
| Pyrene |
<17 |
NQ |
|
NQ |
NQ |
|
<17 |
NQ |
17 |
52 |
| Benz[a]anthracene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| Chrysene |
<2 |
<2 |
|
NQ |
10 |
|
<2 |
<2 |
2 |
10 |
| Benzo[b]fluoranthene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| Benzo[k]fluoranthene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| Benzo[a]pyrene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| Indeno[1,2,3-cd]pyrene |
<13 |
<13 |
|
<13 |
<13 |
|
<13 |
<13 |
13 |
39 |
| Dibenzo[a,h]anthracene |
<13 |
<13 |
|
<13 |
<13 |
|
<13 |
<13 |
13 |
39 |
| Benzo[g,h,I]perylene |
<13 |
<13 |
|
<13 |
<13 |
|
<13 |
<13 |
13 |
39 |
| Benzo[b]thiophene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| 2-methylnaphthalene |
<20 |
<20 |
|
<20 |
<20 |
|
<20 |
<20 |
20 |
46 |
| 1-methylnaphthalene |
<20 |
<20 |
|
<20 |
<20 |
|
<20 |
<20 |
20 |
46 |
| Biphenyl |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| 1-ethylnaphthalene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| 1,2-dimethylnaphthalene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| 4-methylbiphenyl |
<84 |
<84 |
|
<84 |
<84 |
|
<84 |
<84 |
84 |
203 |
| 2,3,5-trimethylnaphthalene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| 1-methylfluorene |
NQ |
<20 |
|
NQ |
NQ |
|
<20 |
<20 |
20 |
46 |
| Dibenzothiophene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| 2-methylphenanthrene |
<2 |
<2 |
|
NQ |
10 |
|
10 |
10 |
2 |
10 |
| 9-methylanthracene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| 3,6-dimethylphenanthrene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| 2-methylfluoranthene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| Benzo[b]naphtho[2,1-d]thiophene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| Benzo[e]pyrene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| Perylene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
| 3-methylcholanthrene |
<2 |
<2 |
|
<2 |
<2 |
|
<2 |
<2 |
2 |
10 |
|
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