|
Limit of detection (LOD) and percentage of nondetects (ND) for 350 samples analyzed at the Wisconsin State Laboratory of Hygiene. |
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| PCB congener (IUPAC*) |
LOD (ng/mL) |
% ND |
PCB congener (IUPAC) |
LOD (ng/mL) |
% ND |
PCB congener (IUPAC) |
LOD (ng/mL) |
% ND |
|
|
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| #5/8 |
1.20 |
100 |
#56/60 |
0.35 |
100 |
#141 |
0.15 |
100 |
| #6 |
0.65 |
100 |
#66/95 |
0.55 |
98.9 |
#146 |
0.20 |
80.3 |
| #7/9 |
0.40 |
100 |
#70/76 |
0.25 |
100 |
#151 |
0.15 |
100 |
| #15/17 |
060 |
100 |
#74 |
0.25 |
80.6 |
#167 |
0.25 |
99.4 |
| #16/32 |
0.55 |
100 |
#77/110 |
0.25 |
100 |
#170/190 |
0.35 |
80.9 |
| #18 |
0.35 |
100 |
#82 |
0.20 |
100 |
#171/202 |
0.15 |
96.0 |
| #19 |
0.40 |
100 |
#84/92 |
0.55 |
100 |
#172/197 |
0.30 |
95.7 |
| #22 |
0.50 |
100 |
#85† |
0.25 |
100 |
#174 |
0.20 |
100 |
| #24/27 |
0.30 |
100 |
#87 |
0.20 |
100 |
#177 |
0.20 |
93.4 |
| #26 |
0.25 |
100 |
#91 |
0.25 |
100 |
#178 |
0.35 |
96.6 |
| #28/31 |
0.60 |
100 |
#97 |
0.15 |
100 |
#180 |
0.20 |
9.7 |
| #33 |
0.25 |
100 |
#99 |
0.25 |
84.3 |
#182/187 |
0.10 |
39.3 |
| #37/42 |
0.30 |
100 |
#101 |
0.30 |
100 |
#183 |
0.15 |
86.3 |
| #40 |
0.30 |
100 |
#105/132/153 |
0.20 |
7.1 |
#185 |
0.15 |
100 |
| #41/71/64 |
0.40 |
100 |
#118 |
0.20 |
57.3 |
#194 |
0.15 |
74.9 |
| #44 |
0.30 |
100 |
#123/149 |
0.15 |
100 |
#195/208 |
0.10 |
92.3 |
| #45 |
0.30 |
100 |
#128 |
0.25 |
100 |
#196/203 |
0.30 |
70.7 |
| #46 |
0.40 |
100 |
#135/144 |
0.30 |
100 |
#199 |
0.15 |
99.7 |
| #47/48 |
0.40 |
100 |
#136† |
0.30 |
100 |
#201 |
0.20 |
56.7 |
| #49 |
0.25 |
100 |
#137/176 |
0.10 |
100 |
#206 |
0.15 |
91.5 |
| #52 |
0.25 |
100 |
#138/163 |
0.25 |
10.8 |
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* International Union of Pure and Applied Chemistry † Interference from contamination prevented determination of concentrations of these congeners in all but 1 sample. The one remaining sample was nondetectable for both congeners. | ||||||||
Weisskopf et al. Environmental Health: A Global Access Science Source 2003 2:2 doi:10.1186/1476-069X-2-2 |
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