Heavy metals in soft tissue of white-tailed eagles found dead or moribund in Germany and Austria from 1993 to 2000

Residues of the potentially toxic metals lead, mercury, and cadmium were analyzed in liver and kidney tissue of 61 free-ranging white-tailed eagles (Haliaeetus albicilla) found dead or moribund in Germany and Austria between 1993 and 2000. Highest values and the widest range were detected for lead in liver and for mercury in kidney tissue. Lead concentrations considered to induce lethal lead poisoning (>5 ppm wet wt) were determined in 28% of liver samples. Lead fragments were detected it the gizzards of two specimens, presumably having died from lead intoxication. Histopathological findings in a recently dead white-tailed eagle indicating acute lead exposure comprise degenerative Purkinje cells in the cerebrellum and inclusion bodies in renal tubular cells. Mercury residues in organs are decreasing compared to former studies in periods when organomercury compounds were used as seed dressing. All cadmium values were low or are at background levels in white-tailed eagles. The present study clearly identities lead as a toxic metal poison in white-tailed eagles in Germany and Austria.     

Congener-specific analysis of polychlorinated biphenyls in white-tailed sea eagles Haliaeetus albicilla collected in Poland

The concentrations of polychlorinated biphenyl (PCBs) congeners including highly toxic non-, mono-, and di-ortho coplanar members as well as their pattern were determined in breast muscles of white-tailed sea eagles collected dead between 1982 and 1990 in Poland. There was a wide variation in total PCB residue concentrations among eagles from various breeding sites, with the Baltic Sea coast registering the highest concentrations. The pattern of PCB residues differed between the eagles examined. Hexa-, hepta-, and pentachlorobiphenyls contributed between 45 and 56%, 18-and 37%, and 9 and 22% in total PCBs, respectively. Toxic equivalents (TEQs) of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) for non-, mono-, and di-ortho coplanar PCBs were very high (8.0–72 g/g wet wt) in white-tailed sea eagles from breeding sites of the coastal area of the southwestern Baltic Sea, and were relatively lower (0.69–4.0 g/g wet wt) in other birds, including two specimens from breeding sites of inland Poland, which died because of acute lead poisoning. PCB IUPAC Nos. 118, 105, 126, and 156 were the highest contributors to the TCDD TEQ of coplanar members, occupying between 39.1 and 57.0%, 9.8 and 17.5%, 7.4 and 22.3%, and 7.0 and 14.2%, respectively. The concentrations of coplanar PCBs in adult white-tailed sea eagles were the highest ever reported in wildlife, but that of total PCBs were similar to those reported in dead eagles from the breeding sites of the coastal area of the northern Baltic in Sweden and Finland in the 1960s and 1970s.     

The contamination of white-tailed sea eagles with organochlorines in Poland

The residues of PCBs, DDTs, HCHs, HCBz, PCBz, CHLs, aldrin, dieldrin, endrin, isodrin, endosulfan 1, endosulfan 2, mirex, TCPM-H and TCPM-OH were determined in breast muscles and an egg of white-tailed sea eagles collected in Poland in 1991-1995. The method of measurement was capillary gas chromatography and low resolution mass spectrometry (HRGC/LRMS) after a non-destructive extraction, clean-up and fractionation of the sample. Only aldrin, endrin, endosulfan 1 and endosulfan 2 were absent in birds and egg examined. Some of the adult white-tailed sea eagles collected dead from the coastal area of the Baltic Sea still remain relatively high contaminated with organochlorines, and the concentrations of PCBs and DDTs in those birds ranged between 2300-2600 and 490-2000 micrograms/g lipids, respectively. In dead egg concentration of PCBs was 390 micrograms/g lipids (25 micrograms/g wet weight), while of DDTs 270 micrograms/g lipids (18 micrograms/g w.w.).     

Accumulation patterns of polychlorinated biphenyl congeners and organochlorine pesticides in Steller's sea eagles and white-tailed sea eagles, threatened species, in Hokkaido, Japan

Polychlorinated biphenyls (PCBs), including coplanar congeners, hexachlorocyclohexane isomers, chlordane-related compounds, and hexachlorobenzene, were found in the breast muscle of Steller's sea eagles (SSE) and white-tailed sea eagles (WSE) threatened species, collected in Hokkaido, Japan, during the two years from 1998 to 1999. Both PCBs and DDTs were the most notable compounds, with concentrations one to two orders of magnitude higher than the other compounds, that is, from 120 to 39,000 and from 68 to 15,000 ng/g wet weight, respectively. Non-ortho (International Union of Pure and Applied Chemistry [IUPAC] 77, 126, and 169) and mono-ortho (IUPAC 105, 118, and 156)-substituted coplanar PCB congeners amounted to 9.2 to 740 pg/g of 2,3,7,8-tetrachlorodibenzo-p-dioxin toxic equivalents derived from the World Health Organization, Paris, France (WHO), toxic equivalent factors. The atmospheric PCBs and DDTs in eastern Siberian cities, such as Khabarovsk and Magadan, have been reported to be much higher than Hokkaido and the North Pacific. Thus, we speculated that the eagles might have been contaminated in these areas, where they spend most of the year except winter, which they spend in eastern Siberia. Adult eagles accumulated more PCBs and DDTs than younger ones. The patterns of PCB congeners were also found to change, depending on the age of the eagle examined; adult eagles showed relatively higher proportions of highly chlorinated PCBs thanjuvenile eagles did. This difference would be related to the efficiency of the excretion and the metabolism of each PCB congener in the eagles.     

Concentrations of Lead in Liver, Kidney, and Bone of Bald and Golden Eagles

The diagnosis of lead poisoning in eagles relies on autopsy information and residue analysis of lead in certain tissues, usually liver or blood. Similarly, the assessment of elevated lead exposure in eagles depends on the determination of lead concentrations in these tissues. Renal and bone lead concentrations have rarely been examined in eagles. We examined relationships among hepatic, renal, and bone lead concentrations in bald and golden eagles from the Canadian prairie provinces. Hepatic and renal lead concentrations were strongly related (R² = 0.87) while those in liver and bone were significantly but poorly related (R² = 0.22). Renal lead concentrations of 5 and 18 μg · g⁻¹ (dry weight) corresponded to hepatic lead concentrations of 6 and 30 μg · g⁻¹, the hepatic concentrations that we used as criterion levels associated with elevated lead exposure and death from lead poisoning, respectively. Lead was elevated in 19 of 119 and 21 of 109 liver and kidney samples, respectively. Of these 19 and 21 liver and kidney samples, 14 and 11, respectively, had lead concentrations compatible with death from lead poisoning. Taken together, lead concentrations were elevated in liver or kidney samples from 25 eagles and were compatible with death from lead poisoning in 15. Mean bone lead was higher in eagles with elevated hepatic lead than in those exhibiting background hepatic lead concentrations. However, even in the former group, bone lead concentrations were lower than those in lead-exposed individuals of other species of birds. Bone is probably not a useful tissue for identifying elevated lead exposure in eagles. Three of eleven birds that had been shot had anomalous renal lead concentrations, suggestive of contamination by residue from lead ammunition. It is important to exclude such birds when assessing lead exposure. Received: 22 October 1998/Accepted: 3 March 1999     

Mercury Contamination in Idaho Bald Eagles, <Emphasis Type="Italic">Haliaeetus leucocephalus</Emphasis>

Because mercury contamination is potentially threatening to bald eagle (Haliaeetus leucocephalus) populations, we collected molted feathers at nests to determine the level of contamination in bald eagles in the state of Idaho, USA. Eagle feathers contained measurable amounts of cadmium (Cd), chromium (Cr), selenium (Se), lead (Pb), as well as mercury (Hg). Cadmium, Cr, Se, and Pb levels averaged 0.17, 4.68, 2.02, and 1.29 mg/kg dry weight, respectively, and were at or below concentrations indicated as causing reproductive failure in bald eagles. Mercury contamination was found to be the highest averaging 18.74 mg/kg dry weight. Although a concentration of only 7.5 mg/kg dry weight Hg in bird feathers can cause reduced productivity and even sterility, all of the eagles we sampled bred successfully and the population of bald eagles continues to grow annually throughout the state.     

Concentrations and Hazard Assessment of Organochlorine Contaminants and Mercury in Smallmouth Bass from a Remote Lake in the Upper Peninsula of Michigan

Concentrations of PCBs, DDTs, toxaphene, chlordanes, dieldrin, and mercury were determined in smallmouth bass (Micropterus dolomieui) collected from Fumee Lake, a remote lake in the Upper Peninsula of Michigan. An ecological hazard assessment was conducted to determine potential impacts of contaminants on bald eagles and mink eating fish from this lake. Concentrations of organochlorines, except toxaphene, and mercury in smallmouth bass were similar to those found in fish from Lake Superior, where atmospheric inputs are the primary sources. Bioaccumulation was indicated by a positive correlation between fish weight and contaminant concentrations for organochlorines, while mercury concentrations did not appear to correspond predictably to body weight. Concentrations of mercury and PCBs in smallmouth bass were sufficiently great to be of concern regarding their consumption by eagles or mink. Received: 16 June 1997/Accepted: 11 August 1997     

Exposure of the Inuit population of Nunavik (Arctic Quebec) to lead and mercury

The authors conducted a survey during 1992 to evaluate blood levels of lead and mercury in Inuit adults of Nunavik (Arctic Quebec, Canada). Blood samples obtained from 492 participants (209 males and 283 females; mean age = 35 yr) were analyzed for lead and total mercury; mean (geometric) concentrations were 0.42 micromol/l (range = 0.04-2.28 micromol/l) and 79.6 nmol/l (range = 4-560 nmol/l), respectively. Concentrations of omega-3 fatty acid in plasma phospholipids--a biomarker of marine food consumption--were correlated with mercury (r = .56, p < .001) and, to a lesser extent, with blood lead levels (r = .31, p < .001). Analyses of variance further revealed that smoking, age, and consumption of waterfowl were associated with lead concentrations (r2 = .30, p < .001), whereas age and consumption of seal and beluga whale were related to total mercury levels (r2 = .30, p < .001). A significant proportion of reproductive-age women had lead and mercury concentrations that exceeded those that have been reportedly associated with subtle neurodevelopmental deficits in other populations.     

Mercury and selected pesticide levels in fish and wildlife of Utah: II. levels of mercury,DDT, DDE,dieldrin and PCB in chukars,pheasants and waterfowl

Summary Levels of mercury and selected pesticides were determined in muscle tissue of chukars, pheasants and waterfowl collected from various regions within the state of Utah. None of the chukar tissue 6% of the pheasant tissue and 4% of the waterfowl tissue analyzed contained mercury concentrations greater than the FDA limit of 0.5 ppm. None of the chukars or pheasants and only 2% of the waterfowl inspected contained dieldrin concentrations above the FDA tolerance level of 0.3 ppm. None of the chukars or pheasants contained levels of DDT + DDE above 5.0 ppm FDA tolerance level. The majority of the waterfowl tissue contained levels of PCB's higher than selected pesticide levels. No definite relationship between the levels of mercury and pesticides or PCB's was noted.     

Mercury levels in tissues of Giant otters (Pteronura brasiliensis) from the Rio Negro, Pantanal, Brazil

This research reports the first data on mercury levels found in Giant otters (Pteronura brasiliensis) from South America. Mercury concentrations were analyzed from different organs/tissues of two animals found dead floating on the water of the Rio Negro in the Pantanal, Brazil. The mean mercury concentration ranged from 2.94 to 3.68 microg/g in hair, from 1.52 to 4.3 microg/g in liver, and from 1.11 to 4.59 microg/g in kidney and was 0.17 microg/g in muscle samples. In comparison with other research, there is no evidence of contamination in these animals and mercury concentrations in tissues appeared to be at levels below those associated with toxicity.     

Mercury Residues in Livers of Bald Eagles (<Emphasis Type="Italic">Haliaeetus leucocephalus</Emphasis>) Found Dead or Dying in British Columbia,Canada (1987–1994)

Postmortem examinations were conducted on 82 bald eagles (Haliaeetus leucocephalus) found dead or dying in British Columbia, Canada, from 1987 to 1994. As part of the examination, livers were analyzed for total mercury (Hg) content, as well as methylmercury (meHg) and selenium (Se) in selected individuals. In total, 67 eagles were classed as having low Hg exposure [total Hg liver residues ranging from 0.5 to 17.2 mg/kg dry weight (dw)]. Fourteen eagles were moderately exposed (liver residues ranging from 19.2 to 36.8 mg/kg Hg dw). One eagle was judged to have died of Hg poisoning, with a total liver Hg content of 130.3 mg/kg dw, of which approximately 77% was meHg. The poisoned eagle and most of the exposed eagles were found in locations where effluent from pulp and paper processing plants is discharged along the British Columbia coast. In total, 6% of eagles examined died as a result of acute metal toxicosis (one from Hg poisoning, four from lead poisoning), in comparison to 72% dying from trauma (electrocution, vehicle/power line collision, eagle attack, trap, gunshot, drowning, and asphyxiation) and 11% from disease. The cause of death was undetermined in the remaining 11% of eagles.     

Retrospective Study of the Diagnostic Criteria in a Lead-Poisoning Survey of Waterfowl

Between 1983 and 1986 the National Wildlife Health Center (NWHC) conducted a nationwide study of lead poisoning of waterfowl from federal and state refuges. This survey was done to assist in identifying zones with lead-poisoning problems. One thousand forty one moribund or dead waterfowl were collected and examined. The presence or absence of 13 gross lesions selected as indicators of lead poisoning and three lesions indicating body condition was recorded. Lead-poisoning diagnoses were based on the finding of at least 6–8 ppm (wet weight) lead in the liver and either lead shot in the gizzard content or at least one convincing gross lesion indicative of lead poisoning. Four hundred twenty-one of these waterfowl were diagnosed as lead poisoned. The NWHC survey provided a comprehensive basis for estimating the sensitivities, specificities, and likelihood ratios of the gross lesions of lead poisoning and the associated hepatic lead concentrations for several species of waterfowl. Some of the 13 defined gross lesions were more common than others; frequencies ranged from 3% to 80% in the 421 lead-poisoned waterfowl. The most reliable indicators of lead poisoning were impactions of the upper alimentary tract, submandibular edema, myocardial necrosis, and biliary discoloration of the liver. Each of the 13 lesions occurred more frequently in the lead-poisoned birds, but each of the lesions also occurred in waterfowl that died of other causes. The number of lead shot present in a bird's gizzard was only weakly correlated with its hepatic lead concentration; however, this weak correlation may have been adequate to account for differences in hepatic lead concentrations among species, once the weights of the species were taken into account. Although lead-poisoned ducks tended to have higher hepatic mean lead concentrations than did lead-poisoned geese or swans, the differences were probably a result of a greater dose of shot per body weight than to kinetic differences between species. Hepatic lead concentrations were independent of age and sex. Ninety-five percent of waterfowl diagnosed as lead poisoned had hepatic lead concentrations of at least 38 ppm dry weight (10 ppm wet weight). Fewer than 1% of the waterfowl that died of other causes had a concentration that high. This fifth percentile, of 38 ppm dry weight (10 ppm wet weight), is a defensible criterion for identifying lead-poisoned waterfowl when interpreting hepatic lead concentrations in the absence of pathological observations. Received: 12 February 1998/Accepted: 22 April 1998     

Use of Skin and Blood as Nonlethal Indicators of Heavy Metal Contamination in Northern Water Snakes (Nerodia sipedon)

Relatively little is known about contaminants in reptiles, particularly snakes. The concentrations of arsenic, cadmium, chromium, lead, manganese, mercury, and selenium were examined in blood and skin of 46 northern water snakes (Nerodia sipedon) in Tennessee and correlated with concentrations in internal tissues (liver, kidney, muscle) to determine if blood or skin could serve as a nonlethal indicator of internal metal exposure or body burden. Snakes were collected from the East Fork Poplar Creek (EFPC) within the United States Department of Energy’s Y-12 National Security Complex (part of the Oak Ridge National Laboratory) and from a reference stretch of the Little River in East Tennessee. For blood, the only consistent positive correlations with internal organs were for mercury, and correlations were low except for muscle. Skin showed significant positive correlations with all three organs for mercury, chromium, selenium, and lead. For manganese and cadmium, skin level was positively correlated with liver level. Blood generally reflects recent exposure, not necessarily body burden, but in water snakes it correlates with body burden for mercury. Skin proved useful for more metals, although patterns were not necessarily consistent across sex and locality subgroups. The most consistent pattern was for mercury, the metal of greatest concern in many aquatic ecosystems, including EFPC.     

Mercury concentrations in three species of fish from North Atlantic offshore waters

Mercury concentrations were determined in tissues and organs of spiny dogfish (Squalus acanthias), cusk (Brosme brosme), and blackbellied redfish (Helicolenus dactylopterus) collected from Atlantic Ocean waters off the northeastern coast of the United States. Information was obtained on the spatial and temporal distribution of mercury in the organs and tissues of these fish.Cusk were obtained from 2 locations and blackbellied redfish from 4 locations. The mercury levels in both muscle and liver of cusk averaged about 0.30 ppm for one and 0.16 ppm for the second location. Gills and kidneys of cusk had mercury levels that averaged 0.08 ppm for both collections. In blackbellied redfish mercury levels in muscle and liver averaged about 0.08 ppm for all locations; gill and kidney tissues of this fish were less than 0.2 ppm.Spiny dogfish were obtained from 5 areas. No significant difference in mercury levels was found in muscle tissue as related to geographic area. Mercury levels ranged from 0.21 to 0.62 ppm. The kidneys of dogfish contained about 54% of the mercury level of muscle. The mercury level in gills of dogfish ranged from 0.06 to 0.21 ppm.Spiny dogfish pups were obtained from 6 adult females. Samples of muscle, liver, gill, kidney, and yolk of pups were analyzed for mercury. These same samples, except for the yolk, were obtained from the adult females. Mercury levels in all pup samples were less than 0.03 ppm, while mercury levels in adult females ranged from 0.03 to 1.1 ppm in all tissues and organs.     

Exposure of the Inuit Population of Nunavik (Arctic Québec) to Lead and Mercury

The authors conducted a survey during 1992 to evaluate blood levels of lead and mercury in Inuit adults of Nunavik (Arctic Québec, Canada). Blood samples obtained from 492 participants (209 males and 283 females; mean age = 35 yr) were analyzed for lead and total mercury; mean (geometric) concentrations were 0.42 μmol/l (range = 0.04–2.28 μmol/l) and 79.6 nmol/l (range = 4–560 nmol/l), respectively. Concentrations of omega-3 fatty acid in plasma phospholipids–a biomarker of marine food consumption–were correlated with mercury (r = .56, p < .001) and, to a lesser extent, with blood lead levels (r = .31, p < .001). Analyses of variance further revealed that smoking, age, and consumption of waterfowl were associated with lead concentrations (r ² = .30, p < .001), whereas age and consumption of seal and beluga whale were related to total mercury levels (r ² = .30, p < .001). A significant proportion of reproductive-age women had lead and mercury concentrations that exceeded those that have been reportedly associated with subtle neurodevelopmental deficits in other populations.     

Metals in Laysan Albatrosses from Midway Atoll

We examined the concentrations of lead, cadmium, selenium, chromium, manganese, arsenic, tin, and mercury in the heart, liver, kidney, salt gland, and feathers of adult (n = 10) and young (n = 15) Laysan albatrosses (Diomedea immutabilis) from Midway Atoll in the north-central Pacific Ocean. Lead poisoning has been reported in some Laysans nesting near buildings on Midway, but other heavy metals have not been examined. We examined tissue distribution of metals by age and gender (adults only). We also examined tissue concentrations in three birds with a droop-wing syndrome characteristic of lead poisoning. We compared metal levels in salt gland (a special excretory organ of marine birds) with those in other tissues. All metals varied significantly across tissues in both adults and chicks, and the relative tissue concentrations were similar in adults and chicks for most metals. Adults had higher levels of most metals in most organs, with significant differences mainly for cadmium (up to 20× higher in kidney and salt gland) and for mercury (17× higher in kidney). However, chicks had significantly higher manganese in liver and arsenic in salt gland. The salt gland had concentrations of most metals (except cadmium, selenium, and mercury) comparable to the kidney levels, which is consistent with it serving as an excretory organ for the cations. Chicks with droop-wings had very elevated levels of lead in their tissue (16.8 ppm in feathers, 14 ppm in liver and kidney), whereas levels of other metals were not significantly different from the apparently normal chicks. Received: 1 April 1999/Accepted: 29 June 1999     

Lead poisoning in waterfowl from the Ebro Delta,Spain: Calculation of lead exposure thresholds for mallards

Lead poisoning in waterfowl was investigated during 1991/92 at the Ebro Delta Natural Park. Sediment examination showed a lead shot concentration available to waterfowl ranging from 60,149 to 544,748 shot pellets/ha in some zones. Examination of gizzards from 108 bird carcasses confirmed that four different species had ingested lead shot. To establish prevalence values for waterfowl, 50 ducks, mainly mallards (Anas platyrhynchos) (n=40), were captured. Examination of the gizzard contents revealed that 25% of the mallards had ingested lead pellets. Lead concentration in liver and kidneys was determined by atomic absorption spectrometry, and the diagnostic concentration values for both of the organs were studied. The mallard population was divided into two groups, based on the presence or absence of lead shots in their gizzards. After a probit transformation of data, threshold values were 1.5 g/g WW in liver and 3.0 g/g WW in kidneys. The results derived from lead concentrations and gizzard examination showed that 27% of the mallards in the winter period were poisoned, which represents about 10,000 individuals of a population of 36,500 mallards in the Ebro Delta.     

Relationship of blood mercury levels to health parameters in the loggerhead sea turtle (Caretta caretta)

BACKGROUND: Mercury is a pervasive environmental pollutant whose toxic effects have not been studied in sea turtles in spite of their threatened status and evidence of immunosuppression in diseased populations. OBJECTIVES: In the present study we investigate mercury toxicity in loggerhead sea turtles (Caretta caretta) by examining trends between blood mercury concentrations and various health parameters. METHODS: Blood was collected from free-ranging turtles, and correlations between blood mercury concentrations and plasma chemistries, complete blood counts, lysozyme, and lymphocyte proliferation were examined. Lymphocytes were also harvested from free-ranging turtles and exposed in vitro to methylmercury to assess proliferative responses. RESULTS: Blood mercury concentrations were positively correlated with hematocrit and creatine phosphokinase activity, and negatively correlated with lymphocyte cell counts and aspartate amino-transferase. Ex vivo negative correlations between blood mercury concentrations and B-cell proliferation were observed in 2001 and 2003 under optimal assay conditions. In vitro exposure of peripheral blood leukocytes to methylmercury resulted in suppression of proliferative responses for B cells (0.1 microg/g and 0.35 microg/g) and T cells (0.7 microg/g). CONCLUSIONS: The positive correlation between blood mercury concentration and hematocrit reflects the higher affinity of mercury species for erythrocytes than plasma, and demonstrates the importance of measuring hematocrit when analyzing whole blood for mercury. In vitro immunosuppression occurred at methylmercury concentrations that correspond to approximately 5% of the individuals captured in the wild. This observation and the negative correlation found ex vivo between mercury and lymphocyte numbers and mercury and B-cell proliferative responses suggests that subtle negative impacts of mercury on sea turtle immune function are possible at concentrations observed in the wild.     

Mercury concentration of fish in Tokyo Bay and the surrounding sea area

Total mercury in the muscles of three fish species was analyzed in fish caught in Tokyo Bay and the surrounding sea areas, Sagami Bay and Choshi. Tokyo Bay is a semi-closed sea area surrounded by Tokyo, Kanagawa and Chiba prefectures. Sagami Bay and Choshi are open to the Pacific Ocean. A total of 412 fish consisting of northern whiting (Sillago japonica), flatfish (Limanda yokohamae) and sardine (Sardinops melanosticta) were caught in these areas over a 6 months period from November 1998 to April 1999. Total mercury concentration ranged from 0.008-0.092 microgram/g (wet wt.) in northern whiting, 0.006-0.065 microgram/g in flatfish and 0.001-0.045 microgram/g in sardine. All concentrations were below the restriction limit of fish mercury in Japan, 0.4 microgram/g of total mercury concentration. A significant correlation was found between mercury concentrations and body length or body weight in northern whiting and flatfish, irrespective of the sea area. A correlation was also found between mercury concentration in fish and their feeding habits: among the 3 species caught in the same area, crustacean feeding northern whiting had the highest, polychaete feeding flatfish moderate, and plankton feeding sardine had the lowest mercury concentration. In a comparison of mercury concentration in the same species caught in different sea areas, a higher concentration was noted in fish caught in the semi-closed sea area of Tokyo Bay, than in fish caught in the open sea areas of Sagami Bay and Choshi. This difference was most marked in fish caught at the bottom of Tokyo Bay and we considered that the mercury concentration of seawater and sediment in these areas was the cause of mercury accumulation in fish. These findings suggest that improved water quality control and environmental monitoring is necessary in semi-closed sea areas such as Tokyo Bay.     

Contaminants in fishes from great lakes-influenced sections and above dams of three Michigan Rivers: III. Implications for health of bald eagles

Recently, there have been discussions of the relative merits of passage of fishes around hydroelectric dams on three rivers (Au Sable, Manistee, and Muskegon) in Michigan. A hazard assessment was conducted to determine the potential for adverse effects on bald eagles that could consume such fishes from above and below dams on the three primary rivers. The hazard assessments were verified by comparing the reproductive productivities of eagles nesting in areas where they ate primarily fish from either above or below dams on the three primary rivers, as well as on two additional rivers in Michigan, the Menominee and Thunder Bay. Concentrations of organochlorine insecticides (OCI), polychlorinated biphenyls (total PCBs), 2,3,7,8-tetrachlorodibenzo-p-dioxin equivalents (TCDD-EQ), and total mercury (Hg) were measured in composite samples of fishes from above and below hydroelectric dams on the Manistee and Muskegon Rivers, which flow into Lake Michigan, and the Au Sable River, which flows into Lake Huron. Mean concentrations of OCI, total PCBs, and TCDD-EQ were all greater in fishes from below the dams than in those from above. The hazard assessment indicated that current concentrations of Hg and OCI other than DDT (DDT + DDE + DDD) in fish from neither above nor below dams would present a significant hazard to bald eagles (Haliaeetus leucocephalus). Both total PCBs and TCDD-EQ in fishes from below the dams currently present a significant hazard to bald eagles, since their mean hazard quotients (HQ) were all greater than one.