Tissue localisation of tetra- and pentabromodiphenyl ether congeners (BDE-47,-85 and -99) in perinatal and adult C57BL mice

被引:49
作者
Darnerud, PO [1 ]
Risberg, S [1 ]
机构
[1] Natl Food Adm Toxicol Lab, Div Toxicol, SE-75126 Uppsala, Sweden
关键词
distribution; rodent; PBDE; C-14-labelled; foetal; breast milk;
D O I
10.1016/j.chemosphere.2005.04.004
中图分类号
X [环境科学、安全科学];
学科分类号
08 [工学]; 0830 [环境科学与工程];
摘要
The distribution of polybrominated diphenyl ether (PBDE) congeners was followed in C57BL mice. The animals were subjected to whole-body autoradiography using C-14-labelled 2,2',4,4'-tetrabromodiphenyl ether (BDE-47), 2,2',3,4,4'-pentabromodiphenyl ether (BDE-85) and 2,2',4,4,5-pentabromodiphenyl ether (BDE-99). Labelled BDE85 and -99 were also used in quantitative studies on milk transfer and tissue concentrations during the neonatal period (12-15 days post partum), by use of liquid scintillation technique. The results show that in adult mice the studied PBDEs were effectively taken up, retained in fatty tissues and concentrated in some specific organs, i.e. the liver, adrenal cortex, ovary, lung and (initially) the brain. At longer post-injection time, the concentration in most tissues was considerably lower, and radioactivity was mainly found in fat depots and the liver. No significant difference in distribution between the three studied congeners was observed. Following maternal exposure, the foetal uptake was limited. On the other hand, during lactation a considerable fraction of the dose (about 20% of the studied penta-BDEs) given to the dam was transferred to the offspring. As in several cases the presently observed organ accumulation corresponds with earlier reports on PBDE effects in the same organs, the present results should be taken into consideration in the risk assessment of this compound group. (c) 2005 Elsevier Ltd. All rights reserved.
引用
收藏
页码:485 / 493
页数:9
相关论文
共 48 条
[1]
An overview of commercially used brominated flame retardants, their applications, their use patterns in different countries/regions and possible modes of release [J].
Alaee, M ;
Arias, P ;
Sjödin, A ;
Bergman, Å .
ENVIRONMENT INTERNATIONAL, 2003, 29 (06) :683-689
[2]
POLYBROMINATED AROMATIC POLLUTANTS FOUND IN FISH IN SWEDEN [J].
ANDERSSON, O ;
BLOMKVIST, G .
CHEMOSPHERE, 1981, 10 (09) :1051-1060
[3]
Effects of perinatal exposure to a polybrominated diphenyl ether (PBDE 99) on mouse neurobehavioural development [J].
Branchi, I ;
Alleva, E ;
Costa, LG .
NEUROTOXICOLOGY, 2002, 23 (03) :375-384
[4]
PCB METHYL SULFONES AND RELATED-COMPOUNDS - IDENTIFICATION OF TARGET-CELLS AND TISSUES IN DIFFERENT SPECIES [J].
BRANDT, I ;
BERGMAN, A .
CHEMOSPHERE, 1987, 16 (8-9) :1671-1676
[5]
BROUWER A, 1990, CHEMOSPHERE, V20, P1257
[7]
Interactions of persistent environmental organohalogens with the thyroid hormone system: Mechanisms and possible consequences for animal and human health [J].
Brouwer, A ;
Morse, DC ;
Lans, MC ;
Schuur, AG ;
Murk, AJ ;
Klasson-Wehler, E ;
Bergman, A ;
Visser, TJ .
TOXICOLOGY AND INDUSTRIAL HEALTH, 1998, 14 (1-2) :59-84
[8]
Burreau S, 1997, ENVIRON TOXICOL CHEM, V16, P2508, DOI [10.1897/1551-5028(1997)016&lt
[9]
2508:DUIPEL&gt
[10]
2.3.CO