Dichlorophenols
sample type |
n<MDC |
n>MDC |
mean>MDC |
std. dev. |
max. |
sediment |
9 |
0 |
- |
- |
- |
water |
109 |
14 |
0.018 |
0.039 |
0.0152 |
fish-muscle |
49 |
69 |
67.6 |
131 |
736 |
fish-liver |
19 |
27 |
44.8 |
38.2 |
207 |
invertebrates |
4 |
0 |
- |
- |
- |
Trichlorophenols
sample type |
n<MDC |
n>MDC |
mean>MDC |
std. dev. |
max. |
sediment |
139 |
16 |
7.39 |
3.8 |
15.1 |
water |
49 |
99 |
0.024 |
0.021 |
0.116 |
fish-muscle |
174 |
88 |
58.1 |
193 |
1442 |
fish-liver |
43 |
12 |
19.8 |
9.55 |
34.5 |
invertebrates |
10 |
17 |
225 |
468 |
2000 |
Tetrachlorophenols
sample type |
n<MDC |
n>MDC |
mean>MDC |
std. dev. |
max. |
sediment |
116 |
132 |
11.0 |
14.5 |
90 |
water |
32 |
174 |
0.705 |
1.66 |
14.8 |
fish-muscle |
65 |
292 |
95.7 |
269 |
2522 |
fish-liver |
30 |
61 |
67.0 |
91.9 |
520 |
invertebrates |
25 |
27 |
388 |
702 |
3000 |
Pentachlorophenol
sample type |
n<MDC |
n>MDC |
mean>MDC |
std. dev. |
max. |
sediment |
128 |
129 |
12.6 |
19.5 |
107 |
water |
40 |
166 |
0.159 |
0.326 |
2.71 |
fish-muscle |
54 |
311 |
134 |
344 |
3200 |
fish-liver |
24 |
67 |
105 |
167 |
1030 |
invertebrates |
24 |
28 |
392 |
907 |
4200 |
Table 3.6.1 (continued)
Total Chlorophenols
sample type |
n<MDC |
n>MDC |
mean>MDC |
std. dev. |
max. |
sediment |
120 |
137 |
23.2 |
29.9 |
180 |
water |
28 |
178 |
0.852 |
1.94 |
17.5 |
fish-muscle |
55 |
315 |
252 |
699 |
6239 |
fish-liver |
24 |
69 |
182 |
246 |
1550 |
invertebrates |
21 |
31 |
816 |
1830 |
9200 |
From Reference 693. Data in µg/L (water) or µg/g (dry for sediments) and (wet for organisms). MDC = minimum detectable concentration; this varies with the sample and the chlorophenol since this is composite data from many sources and analytical techniques.