“…One of the difficulties in characterizing concentrations and sources of toxaphene and chlordane is that they are both extensively biotransformed by mammals and birds [9][10][11][12][13]. The metabolism of toxaphene has been studied in chickens [14] but its metabolism by other avian species has not been investigated [10]. Information on the concentrations of toxaphene and chlordane in avian species generally, and seabirds in particular, is limited.…”
Toxaphene and other persistent organochlorine (OC) pesticides (chlordane-related compounds [CHL], DDT-related compounds [DDT], hexachlorocyclohexanes [HCH], tris(p-chloro-phenyl)methane, hexachlorobenzene, octachlorostyrene, diel-drin) were determined in fat of Laysan albatross (Diomedea immutabilis) and in fat and eggs of blackfooted albatross (Diomedea nigripes) from the central north Pacific Ocean. The HCH isomers and chlordane-and DDT-related compounds were also determined in eggs of northern royal albatross (Diomedea sanfordi) collected in New Zealand. Toxaphene was detected in fat samples at mean standard deviation (SD) levels ranging from 243 61 ng/g wet weight in Laysan albatross to 1,020 237 ng/g wet weight in blackfooted albatross. These levels were higher than CHL and HCH but lower than DDT. In eggs of blackfooted albatross, toxaphene was the major OC pesticide, averaging 513 ng/g wet weight in two pooled samples compared with 293 ng/g wet weight for DDT. Two toxaphene congeners, the octachloroborane B8-1413 (Parlar 26) and the nonachlorobornane B9-1679 (P50), comprised about 38% of total toxaphene in both albatross species. All OC compounds were present at significantly higher levels in blackfooted than Laysan albatross fat with the exception of HCH, dieldrin, and octachlorostyrene. Mean levels of DDT and HCH in northern royal albatross eggs from New Zealand were 4 and 60 times lower, respectively, than in blackfooted albatross eggs. The pattern of OC pesticide accumulation was consistent with differences in distribution of the three species in the Pacific Ocean, with highest levels in blackfooted albatross, which feed off the west coast of North America, intermediate levels in Laysan albatross, which frequent the western Pacific, and lowest levels in northern royal albatross, which are confined to the southern oceans surrounding the Antarctic.
“…One of the difficulties in characterizing concentrations and sources of toxaphene and chlordane is that they are both extensively biotransformed by mammals and birds [9][10][11][12][13]. The metabolism of toxaphene has been studied in chickens [14] but its metabolism by other avian species has not been investigated [10]. Information on the concentrations of toxaphene and chlordane in avian species generally, and seabirds in particular, is limited.…”
Toxaphene and other persistent organochlorine (OC) pesticides (chlordane-related compounds [CHL], DDT-related compounds [DDT], hexachlorocyclohexanes [HCH], tris(p-chloro-phenyl)methane, hexachlorobenzene, octachlorostyrene, diel-drin) were determined in fat of Laysan albatross (Diomedea immutabilis) and in fat and eggs of blackfooted albatross (Diomedea nigripes) from the central north Pacific Ocean. The HCH isomers and chlordane-and DDT-related compounds were also determined in eggs of northern royal albatross (Diomedea sanfordi) collected in New Zealand. Toxaphene was detected in fat samples at mean standard deviation (SD) levels ranging from 243 61 ng/g wet weight in Laysan albatross to 1,020 237 ng/g wet weight in blackfooted albatross. These levels were higher than CHL and HCH but lower than DDT. In eggs of blackfooted albatross, toxaphene was the major OC pesticide, averaging 513 ng/g wet weight in two pooled samples compared with 293 ng/g wet weight for DDT. Two toxaphene congeners, the octachloroborane B8-1413 (Parlar 26) and the nonachlorobornane B9-1679 (P50), comprised about 38% of total toxaphene in both albatross species. All OC compounds were present at significantly higher levels in blackfooted than Laysan albatross fat with the exception of HCH, dieldrin, and octachlorostyrene. Mean levels of DDT and HCH in northern royal albatross eggs from New Zealand were 4 and 60 times lower, respectively, than in blackfooted albatross eggs. The pattern of OC pesticide accumulation was consistent with differences in distribution of the three species in the Pacific Ocean, with highest levels in blackfooted albatross, which feed off the west coast of North America, intermediate levels in Laysan albatross, which frequent the western Pacific, and lowest levels in northern royal albatross, which are confined to the southern oceans surrounding the Antarctic.
“…In chickens as in mammals, orally ingested camphechlor is stored mainly in the fat tissue (Bush et al, 1978). The pattern of residues present in fat 72 hours after oral administration of camphechlor was similar to the original camphechlor pattern, but differed greatly from the hepatic congener profile (Saleh et al, 1979), suggesting that in fat mainly parent compound is stored, whereas in the liver mainly contained camphechlor metabolites. Carry over ratio (concentration in tissue/concentration in feed at steady state) observed in chickens fed camphechlor at doses of 0.22 to 3.82 mg/kg feed for periods up to 8 weeks were: fat 4.9, heart and gizzard 0.16, leg muscle 0.13, kidney 0.09, breast muscle 0.05 and liver 0.03.…”
Section: Birdsmentioning
confidence: 79%
“…Moreover, sulfate and glucuronide conjugates were detected in urine and faeces of rat receiving a single oral dose of 14 C-camphechlor Casida, 1978, Chandurkar andMatsumura, 1979). The metabolism of CHB 32 was investigated in mice, rats, hamsters, guinea pigs, rabbits, monkeys and chicken (Saleh et al, 1979). As for camphechlor, CHB 32 was metabolized to partially dechlorinated products and a small amount was eliminated as unmetabolized parent compound.…”
“…Toxaphene (camphechlor) is a complex mixture of some 177 compounds obtained by chlorinating camphene to a 67-69% chlorine content (Pollock and Kilgore, 1980;Saleh et al, 1979). The identified compounds are actually chlorinated bornanes arising from the Wagner-Meerwein rearrangement of the camphene skeleton, among which the octachloronorbornanes; 2,2,5-endo,6-exo-8,8,9,10octachloro-norbornane (17, Figure 96.7) and 2,2,5-endo, 9,9,Figure 96.7), are highly potent, with mouse ip LD 50 values of 2-3 mg/ kg (Turner et al, 1977).…”
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