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Toxins in Osprey Eggs
an indicator of contaminants in the Fraser
and Columbia River basins |
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Table 1. TEQs (ppt) of industrial organochlorines
in Osprey Eggs upstream and downstream of pulp mills in the Fraser and
Columbia River basins. N column refers to sample size. Data are from L.
Wilson, Canadian Wildlife Service, Environment Canada, Pacific and Yukon
Region, 2002.
Fraser River Basin
|
Year
|
N
|
Dioxin 2378
TCDD
|
Furan 2378
TCDF
|
Other Dioxins/Furans
|
PCBs
|
Total TEQs
|
| Upstream Kamloops |
1991 |
6 |
10.94 |
1.40 |
3.46 |
11.01 |
26.81 |
| |
1992 |
5 |
7.95 |
0.72 |
7.99 |
18.30 |
34.95 |
| |
1997 |
5 |
0.55 |
0.53 |
3.61 |
13.42 |
18.10 |
| |
|
|
|
|
|
|
|
| Downstream Kamloops |
1991 |
5 |
45.97 |
2.51 |
6.52 |
9.38 |
64.37 |
| |
1992 |
5 |
26.77 |
3.72 |
7.34 |
11.14 |
48.97 |
| |
1995 |
1 |
7.77 |
2.76 |
4.93 |
6.28 |
21.74 |
| |
1997 |
5 |
3.60 |
0.88 |
1.62 |
9.75 |
15.85 |
| |
|
|
|
|
|
|
|
Columbia River Basin
|
|
|
|
|
|
|
|
| Upstream Castlegar |
1991 |
10 |
2.23 |
0.95 |
7.18 |
19.39 |
29.74 |
| |
1993 |
5 |
1.70 |
1.66 |
5.32 |
9.07 |
17.75 |
| |
1994 |
5 |
0.89 |
1.15 |
3.54 |
24.93 |
30.51 |
| |
1995 |
1 |
0.58 |
0.05 |
2.28 |
27.28 |
30.19 |
| |
|
|
|
|
|
|
|
| Downstream Castlegar |
1991 |
9 |
13.52 |
15.53 |
12.78 |
48.42 |
90.25 |
| |
1992 |
5 |
16.95 |
34.41 |
10.12 |
49.45 |
110.94 |
| |
1993 |
4 |
20.50 |
24.68 |
6.90 |
21.69 |
73.77 |
| |
1994 |
5 |
20.84 |
21.88 |
12.21 |
25.82 |
80.76 |
| |
1997 |
4 |
5.88 |
2.89 |
1.73 |
26.22 |
36.72 |
| |
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Table 2. DDE levels expressed
as geometric means with range from Osprey eggs collected in the Fraser
and Columbia River basins from 1991 to 2001. Data are from L. Wilson,
2003, Environment Canada, Canadian Wildlife Service, Delta, British Columbia,
Elliott et al. 2002 and Elliott et al. 2000. Note that d/s
and u/s denote downstream and upstream respectively and that N is the
sample size.
River Basin
|
Location
|
Year
|
N |
Mean (mg/kg wet weight)
|
Range
|
| Fraser R. |
d/s Prince George, u/s and d/s Kamloops |
1991 |
15 |
1.26 |
0.11 - 12 |
| |
u/s and d/s Prince George, u/s and d/s Kamloops |
1992 |
20 |
1.43 |
0.25 - 13.9 |
| |
d/s Kamloops |
1995 |
1 |
3.17 |
|
| |
u/s Prince George, Pitt River |
1996 |
5 |
3.89 |
0.81 - 10.0 |
| |
u/s and d/s Kamloops |
1997 |
10 |
0.92 |
0.25 - 7.78 |
| |
Nicola Lake |
1999 |
6 |
0.64 |
0.397 - 0.92 |
| |
Pitt River |
2000 |
5 |
0.7 |
0.17 - 2.15 |
| |
Ootsa Lake |
2001 |
6 |
1.02 |
0.298 - 3.37 |
| |
|
|
|
|
|
| Columbia R. |
u/s and d/s Scookumchuck, u/s and d/s Castlegar |
1991 |
35 |
1.97 |
0.32 - 20 |
| |
d/s Castlegar |
1992 |
5 |
1.78 |
0.59 - 4.32 |
| |
u/s and d/s Castlegar |
1993 |
9 |
3.6 |
1.37 - 11.6 |
| |
u/s Castlegar |
1995 |
1 |
1 |
|
| |
d/s Castlegar |
1997 |
4 |
1.1 |
0.59 - 2.17 |
| |
Golden, Naksup, Kinbasket Lake, Revelstoke and Oliver |
2000 |
24 |
0.75 |
0.11 - 3.58 |
| |
Revelstoke Lake |
2001 |
2 |
0.11 |
0.09 - 0.13 |
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Table 3. Levels of organochlorine
pesticides chlordane and dieldrin in Osprey eggs from the Fraser and Columbia
River basins from 1991 to 1997. The residue levels are geometric means
and are from Elliott et al. 1999. ND denotes below detection. Chlordane
levels are the sum of several chlordane-related compounds.
Pesticide/River Basin
|
Site
|
Year
|
Mean (µg/kg wet weight)
|
95 % confidence interval
|
| Chlordane |
|
|
|
|
| Fraser R. |
downstream of Kamloops |
1991 |
0.1 |
0.01 - 1.47 |
| |
|
1992 |
9 |
4.16 - 19.5 |
| |
|
1995 |
4 |
|
| |
|
1997 |
4 |
1.03 - 15.2 |
| |
|
|
|
|
| Columbia R. |
downstream of Castlegar |
1991 |
28.8 |
21.0 - 39.4 |
| |
|
1992 |
30.2 |
22.2 - 41.1 |
| |
|
1993 |
34.4 |
16.7 - 71.0 |
| |
|
1997 |
9.3 |
5.02 - 17.1 |
| |
|
|
|
|
| Dieldrin |
|
|
|
|
| Fraser R. |
downstream of Kamloops |
1991 |
0.7 |
0.11 - 4.43 |
| |
|
1992 |
2.2 |
0.62 - 7.83 |
| |
|
1995 |
ND |
|
| |
|
1997 |
0.2 |
0.02 - 2.41 |
| |
|
|
|
|
| Columbia R. |
downstream of Castlegar |
1991 |
4.4 |
1.94 - 10.1 |
| |
|
1992 |
1.2 |
0.13 - 11.0 |
| |
|
1993 |
2.5 |
0.77 - 7.94 |
| |
|
1997 |
0.3 |
0.01 - 8.25 |
| |
|
|
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Table 4. Total toxaphene in
plasma of osprey chicks from the Fraser and Columbia River basins in British
Columbia and from Jasper National Park in Alberta, 1999-2001. Data are
from Elliott et al. 2002 and ND denotes below detection.
|
Location
|
Year
|
Geometric Mean (µg/kg wet wt.)
|
Range
|
| Fraser R. Basin |
Nicola Lake |
1999 |
0.001 |
ND - 1.08 |
| |
Ootsa Lake |
2001 |
0.34 |
0.14 - 0.71 |
| |
Pitt River |
2000 |
3.16 |
2.86 - 3.49 |
| |
|
|
|
|
| Columbia R. Basin |
Upper Columbia R. |
2000 |
2.58 |
2.29 - 3.35 |
| |
Nakusp |
2001 |
0.91 |
|
| |
Oliver |
1999 2000 |
1.72 |
0.68 - 3.23 |
| |
|
|
|
|
| Alberta |
Jasper National Park |
1999 2000 |
11.64 |
1.27 - 1722 |
Back
Table 5. Mean concentrations
of total mercury (mg/kg dry weight) in eggs of ospreys collected from
the Fraser and Columbia River basins in British Columbia, expressed as
geometric means with range. Note that d/s and u/s denote downstream and
upstream respectively and that N is the sample size.
Location
|
Year
|
Sample Size
|
Mean
|
Range
|
| Fraser R. Basin |
|
|
|
|
| u/s & d/s Prince George, u/s & d/s Kamloops |
1992 |
20 |
0.454 |
0.1 - 1.35 |
| u/s & d/s Kamloops |
1997 |
10 |
0.411 |
0.18 - 1.09 |
| Nicola Lake |
1999 |
6 |
0.326 |
0.17 - 0.60 |
| Pitt River |
2000 |
5 |
0.515 |
0.32 - 0.86 |
| |
|
|
|
|
| Columbia R. Basin |
|
|
|
|
| u/s & d/s Castlegar |
1991 |
19 |
0.585 |
0.26 - 1.44 |
| d/s Castlegar |
1992 |
5 |
0.493 |
0.26 - 0.79 |
| u/s & d/s Castlegar |
1993 |
9 |
0.496 |
0.3 - 1.08 |
| d/s Castlegar |
1997 |
4 |
0.335 |
0.25 - 0.47 |
| Revelstoke, Nakusp, Oliver, Golden & Kinbasket Lake |
2000 |
24 |
0.349 |
0.11 - 1.91 |
| Revelstoke |
2001 |
2 |
0.987 |
0.704 - 1.38 |
Back
Table 6 . TEQs (ng/kg wet weight)
for Tree Swallow whole body homogenates upstream and downstream of Kamloops
and Prince George pulp mills in 1994. Data is from Harris and Elliott
2000. Note that N is the sample size and prefers to pooled samples.
Year |
N |
Site |
2378
TCDF |
12378 PnCDD |
HxCDDs |
non-ortho PCBs |
other PCDD/Fs |
| 1994 |
3p
|
Kamloops (upstream)
|
1.30
|
0.00
|
0.00
|
3.88
|
0.00
|
|
1994
|
11p
|
Kamloops (downstream)
|
3.17
|
0.00
|
0.01
|
11.67
|
0.00
|
|
1994
|
18p
|
Prince George (upstream)
|
0.58
|
0.00
|
0.00
|
1.34
|
0.00
|
|
1994
|
14p
|
Prince George (downstream)
|
1.10
|
1.78
|
0.47
|
8.20
|
0.22
|
Back
Table 7 . Estimated daily discharge of TCDD and
TCDF in final effluent from BC Fraser River Basin pulp and paper mills.
Data are from G. Bannister, Environmental Protection Branch, Environment
Canada, Pacific and Yukon Region, 1999.
YEAR*
|
TCDD mg/d
|
TCDF mg/d
|
| 1987 |
57 |
703 |
| 1988 |
57 |
692 |
| 1989 |
63 |
602 |
| 1990 |
37 |
392 |
| 1991 |
28 |
196 |
| 1992 |
3.4 |
15.5 |
| 1993 |
1.6 |
22 |
| 1994 |
1.1 |
15.5 |
| 1995 |
1.1 |
4.1 |
| 1996 |
1.6 |
3.4 |
| 1997 |
1.6 |
3.4 |
| 1998 |
1.6 |
3.4 |
* Loading value at January each year.
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Long Range Atmospheric Dispersal
of Contaminants

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Satellite telemetry of ospreys tagged
in BC showing migration routes to wintering sites on the Pacific Coast
of Mexico and in Central and South America.


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Radio Telemetry
Twenty-nine transmitters were attached to Ospreys in the
Pacific Northwest (13 from BC). Most wintered in Mexico and southern Texas,
with one bird from BC wintering in each of Costa Rica, Nicaragua, Panama
and Venezuela. Of the Ospreys that wintered in Mexico, there was a general
trend for most to winter in one of two areas: 31% wintered along the Mexican
Gulf coast, especially the mangrove wetlands of Veracruz and Tabasco while
35% wintered in mangroves along the northwest coast in the states of Sinaloa,
Nayarit and Jalisco.
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References used for this indicator:
- Blais, J.M., D.W. Schindler, D.C. Muir, D.B. Donald and B. Rosenberg.
1998. Accumulation of persistent organochlorines in mountains of western
Canada. Nature, 395: 585-588.
- Donald, D., R. Bailey, R. Crosley, D. Muir, P. Shaw and J. Syrgiannis.
1993. Polychlorinated biphenyls and organochlorine pesticides in the
aquatic environment along the continental divide region of Alberta and
British Columbia. Environment Canada, Western and Northern Region, Water
Quality Branch, Regina, SK, Canada. 98 pp.
- Elliott, J., D.P. Shaw, S. Lee, M. Wayland, L. Wilson and D. Muir.
Persistent Organic Pollutants (POPs) in Fish and Osprey from High Elevations.
Mountain Science Highlights, Centre for Alpine Studies, UBC Forestry
(see http://www.forestry.ubc.ca/alpine/highlights/index.htm).
- Elliott, J., D.P. Shaw and D. Muir. 2002. Factors influencing domestic
and international sources of chlorinated hydrocarbons to fish and ospreys
in British Columbia. Toxic Substance research Initiative, Final Report,
TSRI #224. Vancouver, BC (unpublished).
- Elliott, J.E., L.K. Wilson, C.J. Henny, S.F. Trudeau, F.A. Leighton,
S.W. Kennedy and K.M. Cheng. 2001. Assessment of biological effects
of chlorinated hydrocarbons in osprey chicks. Environ. Toxicol. Chem.
20: 866-879.
- Elliott, J., M.M. Machmer, L.K. Wilson and C.J. Henny. 2000. Contaminants
in ospreys from the Pacific Northwest: II. Organochlorine pesticides,
polychlorinated biphenyls and mercury, 1991-1997. Archiv. Environ. Contan.
Toxicol. 38:93-106.
- Elliott, J.E., M. Machmer, C.J. Henny, L.K. Wilson and R.J. Norstrom.
1998. Contaminants in Ospreys from the Pacific Northwest: I. Trends
and patterns in polychlorinated dibenzo-p-dioxins and dibenzofurans
contaminants in eggs and plasma. Archiv. Environ. Contan. Toxicol. 35:
620-631.
- Evers, D.C., J.D. Kaplan, M.W. Meyer, P.S. Reaman, W.E. Brasselton,
A. Major, N. Burgess and A.M. Scheuhammer. 1998. Geographic trend in
mercury measured in common loon feathers and blood. Environ. Toxicol.
Chem. 17: 173-183.
- Harding, L., M.L. Harris and J.E. Elliott. 1998. Heavy and trace metals
in wild mink (Mustela vison) and river otter (Lutra canadensis)
captured on rivers receiving metals discharges. Bulletin of Environmental
Contamination and Toxicology. 61: 600-607.
- Harris, M.L and J.E. Elliott. 2000. Reproductive success and chlorinated
hydrocarbon contamination in tree swallows (Tachycineta bicolor)
nesting along rivers receiving pulp and paper mill effluent discharges.
Env. Pollut. 110: 307-320.
- Hughes, K.D., P.J. Ewins and K.E. Clark 1997. A comparison of mercury
levels in feathers and eggs of osprey (Pandion haliaetus) in
the North American Great Lakes. Archiv. Environ. Contam. Toxicol. 33:
441-452.
- Kidd, K.A., D.W. Schindler, D.C.G. Muir, W.L. Lockhart and R.H. Hesslein.
1995. High concentrations of toxaphene in fishes from subarctic lake.
Science, 269: 240-242.
- Krümmel, E.M., R.W. Macdonald, L.E. Kimpe, I. Gregory-Eaves,
M.J. Demers, J.P. Smol, B. Finney and J.M. Blais. 2003. Delivery of
pollutants by spawning salmon. Nature 425: 255-256.
- Lichota, G.B., M. McAdie and P.S. Ross. 2003. Endangered Vancouver
Island marmots (Marmota vancouverensis): sentinels of atmospherically
delivered contaminants to British Columbia, Canada. Environmental Toxicology
& Chemistry (in prep).
- Macdonald, R.W., D.P. Shaw and C.B.J. Gray 1998. Contaminants in lake
sediments and fish. In: C. Gray and T. Tuominen, eds. Health of the
Fraser River Aquatic Ecosystem: A Synthesis of Research Conducted Under
the Fraser River Action Plan. Environment Canada, Vancouver, B.C.
DOE FRAP 1998-11.
- Poole, A.F. 1989. Ospreys: A natural and unnatural history. Cambridge
University Press, Cambridge, New York.
- Wiemeyer, S.N., C.M. Bunck and A.J. Krynitsky. 1988. Organochlorine
pesticides, polychlorinated biphenyls and mercury in osprey eggs - 1970-79
and their relationships to shell thinning and productivity. Arch. Environ.
Contam. Toxicol. 17:767-787.
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