COMPARISON OF THE TOXICITY OF SEVERAL POLYCHLORINATED DIBENZO-PARA-DIOXINS AND 2,3,7,8-TETRACHLORODIBENZOFURAN IN EMBRYOS OF THE JAPANESE MEDAKA (ORYZIAS-LATIPES)

被引:44
作者
WISK, JD [1 ]
COOPER, KR [1 ]
机构
[1] RUTGERS STATE UNIV,UNIV MED & DENT NEW JERSEY,ROBERT WOOD JOHNSON MED SCH,PISCATAWAY,NJ 08855
关键词
D O I
10.1016/0045-6535(90)90067-4
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Nine polychlorinated dibenzo-p-dioxins (PCDDs) and 2,3,7,8-tetrachlorodibenzofuran (TCDF) were tested in the Japanese medaka embryo bioassay. Individual embryos were exposed to varying nominal concentrations of a PCDD or 2,3,7,8-TCDF under static conditions. The LC50 with 95% confidence intervals for survival to 3 days post-hatch were as follows: 2,3,7,8-TCDD, 13 (10-17) nanograms (ng)/liter (L) (parts per trillion); 2,3,7,8-TCDF, 16 (12-22) ng/L; 1,2,3,7,8-PeCDD, 27 (23-31) ng/L and 1,2,3,4,7,8-HCDD, 2900 (718-11717) ng/L. Both 1,2,7,8-TCDD and 2,3,7-TriCDD caused a concentration dependent increase in visible lesions from 50 to 50000 ng/L. In the 1,2,7,8-TCDD exposed embryos, lethality was observed only at the highest concentration tested (50000 ng/L). For 2,3,7-TriCDD, there was no concentration related increase in lethality from 50 to 50000 ng/L. At 50000 ng/L, 1,3,6,8-TCDD, 2,8-DCDD and 2,3-DCDD did not cause any visible toxicity. The octachlorodibenzo-p-dioxin congener did not cause any visible toxicity at 10000 ng/L. The toxic PCDDs and 2,3,7,8-TCDF caused the same sequela of lesions in the developing Japanese medaka, suggesting that they may act through a common mechanism. These results demonstrate that 2,3,7,8-TCDF and PCDDs with the four lateral positions chlorine substituted and at least one other position non-substituted are toxic to the Japanese medaka embryo. The structure activity relationship observed here is similar to that observed in guinea pigs, mice and trout eleutheroembryos. © 1990.
引用
收藏
页码:361 / 377
页数:17
相关论文
共 30 条
[21]  
Moore J A, 1979, Ann N Y Acad Sci, V320, P151, DOI 10.1111/j.1749-6632.1979.tb56598.x
[22]   FORMATION OF POLYCHLORINATED DIBENZOFURANS AND DIBENZO-PARA-DIOXINS BY PRODUCTION PROCESSES FOR MAGNESIUM AND REFINED NICKEL [J].
OEHME, M ;
MANO, S ;
BJERKE, B .
CHEMOSPHERE, 1989, 18 (7-8) :1379-1389
[23]   TETRACHLORODIBENZO-PARA-DIOXINS AND TETRACHLORODIBENZOFURANS IN ATLANTIC COAST STRIPED BASS AND IN SELECTED HUDSON RIVER FISH, WATERFOWL AND SEDIMENTS [J].
OKEEFE, P ;
HILKER, D ;
MEYER, C ;
ALDOUS, K ;
SHANE, L ;
DONNELLY, R ;
SMITH, R ;
SLOAN, R ;
SKINNER, L ;
HORN, E .
CHEMOSPHERE, 1984, 13 (08) :849-860
[24]   2,3,7,8-TETRACHLORODIBENZO-PARA-DIOXIN AND RELATED HALOGENATED AROMATIC-HYDROCARBONS - EXAMINATION OF THE MECHANISM OF TOXICITY [J].
POLAND, A ;
KNUTSON, JC .
ANNUAL REVIEW OF PHARMACOLOGY AND TOXICOLOGY, 1982, 22 :517-554
[25]   OVERVIEW ON ENVIRONMENTAL FATE OF CHLORINATED DIOXINS AND DIBENZOFURANS - SOURCES, LEVELS AND ISOMERIC PATTERN IN VARIOUS MATRICES [J].
RAPPE, C ;
ANDERSSON, R ;
BERGQVIST, PA ;
BROHEDE, C ;
HANSSON, M ;
KJELLER, LO ;
LINDSTROM, G ;
MARKLUND, S ;
NYGREN, M ;
SWANSON, SE ;
TYSKLIND, M ;
WIBERG, K .
CHEMOSPHERE, 1987, 16 (8-9) :1603-1618
[28]   ABNORMAL CIRCULATORY DEVELOPMENT IN MEDAKA CAUSED BY THE INSECTICIDES CARBARYL, MALATHION AND PARATHION [J].
SOLOMON, HM ;
WEIS, JS .
TERATOLOGY, 1979, 19 (01) :51-62
[29]   2,3,7,8-TETRACHLORODIBENZO-PARA-DIOXIN TOXICITY IN YELLOW PERCH (PERCA-FLAVESCENS) [J].
SPITSBERGEN, JM ;
KLEEMAN, JM ;
PETERSON, RE .
JOURNAL OF TOXICOLOGY AND ENVIRONMENTAL HEALTH, 1988, 23 (03) :359-383
[30]  
WISK JD, UNPUB TOXICOL ENV CH