|
|
|
 |
 |
 |
Toxins in Great Blue Herons
Eggs
an indicator of contaminants in the Georgia
Basin |
 |
 |
Back
Map of the Great Blue Heron Colonies
in the Georgia Basin
Since the late 1970s, Environment Canada has measured
toxin levels at 21 colonies in the Georgia Basin. Of these colonies, three
areas were chosen for in-depth monitoring, reflecting urban (UBC), industrial
(Crofton) and rural (Nicomekl) habitats.

UBC
A colony in the UBC Endowment Lands was chosen to represent non-point
source urban influences. This site is in a 763 ha urban park near Greater
Vancouver (which contains over 1.8 million people). Herons from the UBC
colony forage primarily in the slower waters of the lower Fraser River
and its estuary, as well as along the Spanish Banks shoreline. Thus, the
toxin load experienced by these herons reflects industrial development
throughout the Fraser Basin, including ten pulp and paper mills, as well
as urban influences from the City of Vancouver.
Crofton
A heron colony at Crofton was the principal study population
to examine the effects of toxins from the pulp and paper industry. This
colony was located on a small island north of log-sorting grounds, about
1 km from a bleached kraft pulp and paper mill. Herons were routinely
observed feeding in the intertidal area adjacent to the underwater effluent
discharge pipeline.
Nicomekl
The Nicomekl River colony was chosen to reflect the rural environment,
and as such is a reference population geographically removed from both
urban environments and pulp and paper mills. It is located in a rural
agricultural setting, but away from intensively managed croplands. Herons
from Nicomekl fed in the eelgrass-dominated intertidal zone of Mud and
Boundary Bays. Although near to the Fraser River, the waters of these
feeding grounds are isolated from the estuary and river mixing zones by
oceanographic processes.
Back
Map of the Fraser River Watershed and
Georgia Basin

Back
Organochlorine pesticides in
Great Blue Heron eggs
DDE in mg per kg wet weight
|
|
UBC Urban
|
Nicomekl Rural
|
Crofton Industrial
|
| 1977 |
2.82 |
0.914 |
|
| 1978 |
|
|
|
| 1979 |
|
|
|
| 1980 |
|
|
|
| 1981 |
|
|
|
| 1982 |
2.38 |
|
|
| 1983 |
0.718 |
0.718 |
0.333 |
| 1984 |
|
|
|
| 1985 |
2.97 |
|
|
| 1986 |
0.347 |
0.697 |
0.168 |
| 1987 |
0.87 |
|
0.145 |
| 1988 |
0.587 |
0.66 |
0.122 |
| 1989 |
0.531 |
0.432 |
0.117 |
| 1990 |
1.12 |
0.54 |
0.107 |
| 1991 |
0.808 |
|
0.108 |
| 1992 |
0.43 |
|
0.086 |
| 1993 |
1.62 |
|
0.327 |
| 1994 |
1.02 |
|
0.093 |
| 1995 |
|
|
0.102 |
| 1996 |
0.926 |
|
|
| 1997 |
|
|
|
| 1998 |
0.338 |
|
|
| 1999 |
|
0.212 |
|
| 2000 |
0.359 |
|
|
Dieldrin in mg per kg wet weight
|
|
UBC Urban
|
Nicomekl Rural
|
Crofton Industrial
|
| 1977 |
0.098 |
0.029 |
|
| 1978 |
|
|
|
| 1979 |
|
|
|
| 1980 |
|
|
|
| 1981 |
|
|
|
| 1982 |
0.153 |
|
|
| 1983 |
0.035 |
0.035 |
0.005 |
| 1984 |
|
|
|
| 1985 |
0.258 |
|
|
| 1986 |
0.014 |
0.027 |
0.007 |
| 1987 |
0.083 |
|
0.009 |
| 1988 |
0.034 |
0.04 |
0.007 |
| 1989 |
0.019 |
0.019 |
0.009 |
| 1990 |
0.017 |
0.017 |
0.007 |
| 1991 |
0.013 |
|
0.008 |
| 1992 |
0.011 |
|
0.0 |
| 1993 |
0.054 |
|
0.008 |
| 1994 |
0.018 |
|
0.003 |
| 1995 |
|
|
0.0 |
| 1996 |
0.058 |
|
|
| 1997 |
|
|
|
| 1998 |
0.009 |
|
|
| 1999 |
|
|
|
| 2000 |
0.016 |
0.013 |
|
Chlordane in mg per kg wet weight
|
|
UBC Urban
|
Nicomekl Rural
|
Crofton Industrial
|
| 1977 |
0.01 |
0.026 |
|
| 1978 |
|
|
|
| 1979 |
|
|
|
| 1980 |
|
|
|
| 1981 |
|
|
|
| 1982 |
0.066 |
|
|
| 1983 |
0.028 |
0.028 |
0.006 |
| 1984 |
|
|
|
| 1985 |
0.062 |
|
|
| 1986 |
0.014 |
0.024 |
0.009 |
| 1987 |
0.033 |
|
0.012 |
| 1988 |
0.02 |
0.002 |
0.006 |
| 1989 |
0.021 |
0.003 |
0.006 |
| 1990 |
0.013 |
0.002 |
0.006 |
| 1991 |
0.028 |
|
0.012 |
| 1992 |
0.013 |
|
0.006 |
| 1993 |
0.031 |
|
0.008 |
| 1994 |
0.027 |
|
0.005 |
| 1995 |
|
|
0.004 |
| 1996 |
0.022 |
|
|
| 1997 |
|
|
|
| 1998 |
0.018 |
|
|
| 1999 |
|
0.0009 |
|
| 2000 |
0.011 |
|
|
Toxic Equivalents (TEQs) of industrial
organochlorines in Great Blue Herons eggs
|
Urban (non-point source) UBC Colony
|
|
Dioxin 2378TCDD
|
Furan 2378TCDF
|
Other Dioxins/Furans
|
PCBs
|
| 1977 |
* |
* |
* |
957 |
| 1978 |
|
|
|
|
| 1979 |
|
|
|
|
| 1980 |
|
|
|
|
| 1981 |
|
|
|
|
| 1982 |
* |
* |
* |
620 |
| 1983 |
15 |
11 |
216.1 |
65.23 |
| 1984 |
|
|
|
|
| 1985 |
21.22 |
0.7 |
208.51 |
239.53 |
| 1986 |
24.84 |
3.62 |
183.05 |
94.76 |
| 1987 |
54.49 |
17.03 |
131.73 |
136.65 |
| 1988 |
85.45 |
5.72 |
76.44 |
156.93 |
| 1989 |
159 |
29 |
282.6 |
83.46 |
| 1990 |
45.48 |
7.53 |
131.03 |
102.75 |
| 1991 |
29 |
4 |
99.58 |
178.57 |
| 1992 |
9.19 |
1.38 |
10.74 |
90.86 |
| 1993 |
9.7 |
0.15 |
71.21 |
170.01 |
| 1994 |
4.39 |
1.16 |
33.86 |
142.57 |
| 1995 |
|
|
|
|
| 1996 |
6.16 |
0.85 |
45.13 |
173.15 |
| 1997 |
|
|
|
|
| 1998 |
3.55 |
0.51 |
24.16 |
43.44 |
Rural (non-point source) Nicomekl Colony
|
|
Dioxin 2378TCDD
|
Furan 2378TCDF
|
Other Dioxins/Furans
|
PCBs
|
| 1977 |
* |
* |
* |
161 |
| 1978 |
|
|
|
|
| 1979 |
|
|
|
|
| 1980 |
|
|
|
|
| 1981 |
|
|
|
|
| 1982 |
|
|
|
|
| 1983 |
7 |
3 |
49 |
85.6 |
| 1984 |
|
|
|
|
| 1985 |
|
|
|
|
| 1986 |
10 |
0 |
40 |
92.1 |
| 1987 |
|
|
|
|
| 1988 |
9 |
0 |
7 |
56.2 |
| 1989 |
39 |
2 |
88 |
74.7 |
| 1990 |
18 |
3 |
30 |
86.7 |
| 1991 |
|
|
|
|
| 1992 |
|
|
|
|
| 1993 |
|
|
|
|
| 1994 |
|
|
|
|
| 1995 |
|
|
|
|
| 1996 |
|
|
|
|
| 1997 |
|
|
|
|
| 1998 |
|
|
|
|
| 1999 |
|
|
|
31.2 |
Industrial (point source) Crofton Colony
|
|
Dioxin 2378TCDD
|
Furan 2378TCDF
|
Other Dioxins/Furans
|
PCBs
|
| 1977 |
|
|
|
|
| 1978 |
|
|
|
|
| 1979 |
|
|
|
|
| 1980 |
|
|
|
|
| 1981 |
|
|
|
|
| 1982 |
|
|
|
|
| 1983 |
40 |
24 |
813.42 |
22.59 |
| 1984 |
|
|
|
|
| 1985 |
|
|
|
|
| 1986 |
65.56 |
2.16 |
520.57 |
80.14 |
| 1987 |
209.12 |
3.44 |
603.9 |
68.6 |
| 1988 |
170.09 |
5.53 |
459.84 |
71.38 |
| 1989 |
77.69 |
5.34 |
453.4 |
59.65 |
| 1990 |
102 |
10 |
515.7 |
72.62 |
| 1991 |
16.03 |
2.35 |
113.71 |
33.79 |
| 1992 |
19.4 |
4.6 |
96.06 |
43.23 |
| 1993 |
|
|
|
|
| 1994 |
3.71 |
1.45 |
32.16 |
22.45 |
| 1995 |
|
|
|
|
| 1996 |
|
|
|
|
| 1997 |
|
|
|
|
| 1998 |
|
|
|
|
* denotes years where TEQ values for dioxins and furans were not measured.
Back
References used
in the Toxins in Great Blue Heron Eggs indicator:
- Bellward, G.D., R.J. Norstrom, P.E. Whitehead, J.E. Elliott, S.M.
Bandiera, C. Dworschak, T. Chang, S. Forbes, B. Cadario, L.E. Hart and
K.M. Cheng. 1990. Comparison and polychlorinated dibenzodioxin levels
with hepatic mixed-function oxidase induction in Great Blue Herons.
Journal of Toxicology and Environmental Health. 30:33-52.
- Custer, T.W., G.L. Hensler and T.K. Kaiser. 1983. Clutch size, reproductive
success, and organochlorine contaminants in Atlantic coast Black-crowned
Night Herons. Auk 100:699-710.
- Elliott, J.E., R.W. Butler, R.J. Norstrom and P.E. Whitehead. 1989.
Environmental contaminants and reproductive success of great blue herons
(Ardea herodias) in British Columbia, 1986-1989. Environ. Pollut.
59:91-114.
- Elliott, J.E., R.J. Norstrom and J. Smith, 1996. Patterns, trends
and toxicological significance of chlorinated hydrocarbon and mercury
contaminants in Bald Eagle eggs from the Pacific coast of Canada. Archiv.
Environ. Contam. Toxicol. 31:354-367.
- Elliott, J.E., M.L. Harris, L.K. Wilson, P.E. Whitehead and R.J. Norstrom.
2001. Monitoring temporal and spatial trends in polychlorinated dibenzo-p-dioxins
(PCDDs) and dibenzofurans (PCDFs) in eggs of Great Blue Heron (Ardea
herodias) on the coast of British Columbia, Canada, 1983-1998. Ambio
Vol. 30 No. 7, 416-428 Nov. 2001.
- Elliott, J.E., 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 TSRI # 224.
64pp.
- Harris, M.L., J.E. Elliott, R.W. Butler and L.K. Wilson. 2002. Reproductive
success and chlorinated hydrocarbon contamination of resident great
blue herons (Ardea herodias) from Coastal British Columbia, Canada,
1977 to 2000. Environmental Pollution 121: 207-227.
- Hart, L.E., K.M. Cheng, P.E. Whitehead, K.M. Shah, R.J. Lewis, S.R.
Rushkowski, R.W. Blair, D.C. Bennett, S.M. Bandiera, R.J. Norstrom and
G.D. Bellward. 1991. Dioxin contamination and growth and development
in Great Blue Heron embryos. Journal of Toxicology and Environmental
Health. 32:331-344.
- Hoffman, D.J., B.A. Rattner, C.M. Bunck, A. Krynitsky, H.M. Ohlendorf
and R.W. Loew. 1986. Association between PCBs and lower embryonic weight
in Black-crowned Night Herons in San Francisco Bay. J. Toxicol. Environ.
Health 19:383-391.
- Moul, I.E. 1990. Environmental contaminants, disturbance and breeding
failure at a Great Blue Heron colony on Vancouver Island. M.Sc. thesis,
University of British Columbia, Vancouver, BC. 59pp.
- Sanderson, J.T., J.E. Elliott, R.J. Norstrom, P.E. Whitehead, L.E.
Hart, K.M. Cheng and G.D. Bellward. 1994. Monitoring biological effects
of polychlorinated dibenzo-p-dioxins, dibenzofurans and biphenyls in
Great Blue Heron chicks (Area herodias) in British Columbia.
J. Toxicol. Environ. Health. 41:435-450.
- Wilson, L.K., J.E. Elliott and P.E. Whitehead. 1996. Chlorinated compounds
in wildlife from the Fraser River Basin. Technical Report Series Number
251. Pacific and Yukon Region, Canadian Wildlife Service, Environmental
Conservation Branch. 73pp.
Back
|