Kodavanti P R, Ward T R, Derr-Yellin E C, Mundy W R, Casey A C, Bush B, Tilson H A
National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency, Research Triangle Park, North Carolina, 27711, USA.
Toxicol Appl Pharmacol. 1998 Dec;153(2):199-210. doi: 10.1006/taap.1998.8534.
Our previous in vitro studies with both isolated organelles and primary neuronal cell cultures found that intracellular signal transduction can be perturbed by some noncoplanar PCBs at exposure levels of </=10 microM. However, it is not clear whether such concentrations are achievable in brain in vivo. Also, the pattern of congener disposition and quantities of the PCB accumulation in tissues of animals exposed to commercial PCB mixtures is not well studied. In the present study, we have conducted PCB congener-specific analysis in different brain regions, liver, blood, and fat of adult male Long-Evans rats dosed orally with Aroclor 1254 (0 or 30 mg/kg/day; once per day, 5 days/week for 4 weeks) in corn oil. Twenty-four hours after the last dose, rats were euthanized, and the brains were removed and dissected to obtain cerebellum, frontal cortex, and striatum. Liver, blood, and fat samples were also collected at the same time. Congener-specific analysis of PCBs was performed by high-resolution gas chromatography with electron capture detection. While PCB concentrations in control rat brain regions were less than 0.02 ppm, total PCB congeners in treated animals accumulated to much higher levels. Total levels in the frontal cortex, cerebellum, and striatum were 15.1 +/- 0.3, 13.1 +/- 1.7, and 8.2 +/- 2.6 ppm, respectively. The levels of PCBs in the fat, liver, and blood were 0.041, 0.002, and 0.001 ppm in control rats and 552, 38.3, and 1.6 ppm in treated rats, respectively. In addition to the differential total uptake between tissues, there was differential accumulation of PCBs with respect to the number of chlorines. In all the tissues, the more lightly chlorinated (tetra- and penta-) congeners accumulated less than their respective proportions in the parent Aroclor 1254 mixture. On the other hand, heavily chlorinated (hexa- to nona-) congeners accumulated more than the proportion of these congeners found in Aroclor 1254 mixture. This shift toward accumulation of heavily chlorinated congeners seems to be more pronounced in the brain than liver and fat. Predominant congeners (5-32% of total PCBs) detected in different brain regions, blood, liver, and fat are: 2,3,3',4',5,6- (no. 163) + 2,2',3,4,4',5- (no. 138) (coeluted); 2,2',4,4',5,5'- (no. 153) + 2, 2',3,3',4,6'- (no. 132) (coeluted); 2,3,3',4,4',5- (no. 156) + 2,2', 3,3',4,4',6- (no. 171) (coeluted); 2,3',4,4',5- (no. 118); 2,2',4,4', 5-(no. 99); and 2,3,3',4,4'- (no. 105). These congeners together accounted for about two thirds of the total PCB load in brain. All these predominant congeners are ortho-substituted and therefore are noncoplanar in nature. The total PCB concentrations accumulated in brain were as high as 50 microM (based on average molecular weight of 326.4 for Aroclor 1254) and, at these concentrations, intracellular second messengers were significantly affected in neuronal cultures and brain homogenate preparations in vitro. These results indicate that concentrations that altered Ca2+ disposition and second messenger systems in vitro are achievable in brain in vivo following repeated exposure.
我们之前使用分离细胞器和原代神经元细胞培养物进行的体外研究发现,细胞内信号转导在暴露水平≤10微摩尔时会受到某些非共面多氯联苯的干扰。然而,目前尚不清楚在体内大脑中是否能达到这样的浓度。此外,对于暴露于商业多氯联苯混合物的动物组织中同系物的分布模式和多氯联苯积累量的研究还不够充分。在本研究中,我们对成年雄性Long-Evans大鼠进行了如下实验:用玉米油口服给予Aroclor 1254(0或30毫克/千克/天;每天一次,每周5天,共4周),之后对其不同脑区、肝脏、血液和脂肪进行多氯联苯同系物特异性分析。在最后一次给药24小时后,将大鼠安乐死,取出大脑并解剖以获得小脑、额叶皮质和纹状体。同时也采集了肝脏、血液和脂肪样本。通过带有电子捕获检测的高分辨率气相色谱法对多氯联苯进行同系物特异性分析。对照大鼠脑区中的多氯联苯浓度低于0.02 ppm,而处理组动物体内的多氯联苯同系物总量积累到了更高水平。额叶皮质、小脑和纹状体中的总量分别为15.1±0.3、13.1±1.7和8.2±2.6 ppm。对照大鼠脂肪、肝脏和血液中的多氯联苯水平分别为0.041、0.002和0.001 ppm,处理组大鼠则分别为552、38.3和1.6 ppm。除了不同组织间总摄取量存在差异外,多氯联苯在氯原子数量方面的积累也存在差异。在所有组织中,氯原子含量较低的(四氯和五氯)同系物积累量低于它们在母体Aroclor 1254混合物中的各自比例。另一方面,氯原子含量高的(六氯至九氯)同系物积累量高于在Aroclor 1254混合物中这些同系物的比例。这种向高氯代同系物积累的转变在大脑中似乎比在肝脏和脂肪中更为明显。在不同脑区、血液、肝脏和脂肪中检测到的主要同系物(占多氯联苯总量的5 - 32%)为:2,3,3',4',5,6 - (编号163) + 2,2',3,4,4',5 - (编号138)(共洗脱);2,2',4,4',5,5'- (编号153) + 2, 2',3,3',4,6'- (编号132)(共洗脱);2,3,3',4,4',5 - (编号156) + 2,2', 3,3',4,4',6 - (编号171)(共洗脱);2,3',4,4',5 - (编号118);2,2',4,4', 5 - (编号99);以及2,3,3',4,4'- (编号105)。这些同系物一起约占大脑中多氯联苯总负荷的三分之二。所有这些主要同系物都是邻位取代的,因此本质上是非共面的。大脑中积累的多氯联苯总浓度高达50微摩尔(基于Aroclor 1254的平均分子量326.4),在这些浓度下,体外神经元培养物和脑匀浆制剂中的细胞内第二信使受到了显著影响。这些结果表明,在反复暴露后,体内大脑中能够达到在体外改变钙离子分布和第二信使系统的浓度。