|
Site |
1 |
2 |
3 |
4 |
5 |
6 |
7A |
7B |
|
Location |
Androscoggin |
Androscoggin |
Androscoggin |
Bay |
Bay |
Bay |
Bay |
Bay |
|
Aldrin |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Alpha BHC |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Beta BHC |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Delta BHC |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Alpha-Chlordane |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Gamma-Chlordane |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Dieldrin |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Endosulfan I |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Endosulfan II |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Endosulfan Sulfate |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Endrin |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Endrin Aldehyde |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Endrin Ketone |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Heptachlor Epoxide |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Lindane (Gamma BHC) |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
PP'DDE |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
PP'DDT |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
PP'DDD |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Toxaphene |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Trans-Nonachlor |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
Hexachlorobenzene |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
8 |
9A |
9B |
10 |
11 |
12 |
ER-L |
ER-M |
|
Kennebec |
Kennebec |
Kennebec |
Kennebec |
Kennebec |
Kennebec |
|
|
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
0.5 |
6 |
|
ND |
ND |
ND |
ND |
ND |
ND |
0.5 |
6 |
|
ND |
ND |
ND |
ND |
ND |
ND |
0.02 |
8 |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
0.02 |
45 |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
2 |
15 |
|
ND |
ND |
ND |
ND |
ND |
ND |
3 |
350 |
|
ND |
ND |
ND |
ND |
ND |
ND |
2 |
20 |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
|
ND |
ND |
ND |
ND |
ND |
ND |
-- |
-- |
ER-L represents concentration reported as toxic in 10% of literature.
ER-M represents concentration reported as toxic in 50% of literature.
(Source: Long and Morgan 1990)