|
| Analyzed SRM 1974
|
|
| (n= 15)
|
| Individual PCB Isomers
| Sample no. :
| 59-285
| 59-294
| 59-407
| 59-441
| 59-595
| 59-727
| Mean
| RSD
|
|---|
|
|---|
| | | | |
|
| 2,2',5-trichlorobiphenyl (no. 18) * | | 3 | 4 | 5 | 4 | 5 | 5 | 4 | 30
|
| 2,4,4'-trichlorobiphenyl (no. 28) | | 19 | 25 | 18 | 17 | 55 | 16 | 19 | 35
|
| 2,2',3,5'-tetrachlorobiphenyl (no. 44) | | 10 | 13 | 10 | 9 | 14 | 12 | 10 | 20
|
| 2,2',5,5'-tetrachlorobiphenyl (no. 52) | | 15 | 18 | 15 | 14 | 15 | 17 | 16 | 15
|
| 2,3',4,4'-tetrachlorobiphenyl (no. 66) | | 23 | 29 | 22 | 21 | 54 | 18 | 24 | 18
|
| 2,2',4,5,5'-pentachlorobiphenyl (no. 101) | | 16 | 18 | 16 | 16 | 20 | 20 | 18 | 22
|
| 2,3,3'4,4'-pentachlorobiphenyl (no. 105) | | 5 | 7 | 4 | 4 | 10 | 6 | 7 | 110
|
| 2,3',4,4',5-pentachlorobiphenyl (no. 118) | | 15 | 18 | 15 | 14 | 16 | 19 | 16 | 19
|
| 2,2',3,3',4,4'-hexachlorobiphenyl (no. 128) | | 2 | 3 | 2 | 2 | 5 | 3 | 2 | 32
|
| 2,2',3,4,4',5'-hexachlorobiphenyl (no. 138) | | 14 | 17 | 15 | 15 | 18 | 19 | 16 | 21
|
| 2,2',4,4',5,5'-hexachlorobiphenyl (no. 153) | | 19 | 20 | 20 | 19 | 17 | 27 | 20 | 22
|
| 2,2',3,3',4,4',5-heptachlorobiphenyl (no. 170) | | 0.6 | 0.8 | 0.7 | 0.7 | 2 | nd | 0.7 | 36
|
| 2,2',3,4,4',5,5'-heptachlorobiphenyl (no. 180) | | 1 | 2 | 2 | 2 | 3 | 3 | 2 | 43
|
| 2,2',3,4',5,5',6-heptachlorobiphenyl (no. 187) | | 3 | 3 | 4 | 4 | 4 | 6 | 4 | 25
|
| 2,2',3,3',4,4',5,6-octachlorobiphenyl (no. 195) | | nd | nd | 0.4 | 0.3 | 0.5 | nd | 0.5 | 99
|
| 2,2',3,3',4,4',5,5',6-nonachlorobiphenyl (no. 206) | | nd | 0.2 | 0.4 | 0.8 | 0.2 | nd | 0.4 | 76
|
| 2,2',3,3',4,4',5,5',6,6'-decachlorobiphenyl (no. 209) | | nd | nd | nd | 0.2 | 0.1 | nd | 0.9 | 110
|
|
|---|
* The accepted numbering system for PCB isomers as developed by Ballschmiter and Zell (1980).