Patterson D G, Todd G D, Turner W E, Maggio V, Alexander L R, Needham L L
Division of Environmental Health Laboratory Sciences, Centers for Disease Control and Prevention, Atlanta, GA 30333.
Environ Health Perspect. 1994 Jan;102 Suppl 1(Suppl 1):195-204. doi: 10.1289/ehp.94102s1195.
We have measured non-ortho-substituted (coplanar) polychlorinated biphenyl (PCB) levels as well as polychlorinated dibenzo-p-dioxin (PCDD) and polychlorinated dibenzofuran (PCDF) levels in human adipose tissue and serum collected in Atlanta, Georgia. The results show that the concentrations of the coplanar PCBs can be more than an order of magnitude higher than the concentrations of 2,3,7,8-tetrachlorodibenzo-p-dioxin. Our measurements in pooled serum collected in 1982, 1988, and 1989 show a decrease in coplanar PCB levels from 1982 to 1989. We found that the pattern of relative amounts of coplanar PCBs in adipose tissue varied greatly from person to person unlike the PCDD and PCDF patterns, which were more nearly the same. Age was significantly correlated with the concentrations of 2,3,7,8-TCDD,3,3'4,4'-PCB, 3,3',4,4',5-PCB, and 3,3'4,4',5,5'-PCB in adipose tissue. We also measured levels of the mono- and di-ortho chlorine-substituted PCBs in human serum. The levels for some of these PCB congeners were three orders of magnitude higher than the coplanar PCBs, PCDDs, and PCDFs. We used the international toxicity equivalency factors (TEFs) for PCDDs and PCDFs and the TEFs proposed by Safe for PCBs to calculate the 2,3,7,8-TCDD equivalents. Four PCBs (3,3',4,4',5-; 2,3',4,4',5-;2,3,3',4,4'-;2,3,3',4,4',5-) make a larger contribution than 2,3,7,8-TCDD, while four other PCBs (3,3',4,4'5,5'-; 2,2',3,4,4',5'-;2,2',4,4',5,5'-;2,2',3,4,4',5,5'-) make nearly the same contribution as 2,3,7,8-TCDD. The mono-ortho-chlorine-substituted 2,3',4,4',5-PCB, however, is the major contributor to the total 2,3,7,8-TCDD equivalents in general population samples from the United States, Sweden, and Japan.(ABSTRACT TRUNCATED AT 250 WORDS)
我们测定了佐治亚州亚特兰大市采集的人体脂肪组织和血清中未邻位取代(共平面)的多氯联苯(PCB)水平以及多氯二苯并对二恶英(PCDD)和多氯二苯并呋喃(PCDF)水平。结果表明,共平面多氯联苯的浓度可能比2,3,7,8 - 四氯二苯并对二恶英的浓度高出一个数量级以上。我们对1982年、1988年和1989年采集的混合血清进行的测量显示,从1982年到1989年共平面多氯联苯水平有所下降。我们发现,脂肪组织中共平面多氯联苯的相对含量模式因人而异,这与多氯二苯并对二恶英和多氯二苯并呋喃的模式不同,后者更为相近。年龄与脂肪组织中2,3,7,8 - TCDD、3,3',4,4'-PCB、3,3',4,4',5 - PCB和3,3',4,4',5,5'-PCB的浓度显著相关。我们还测量了人体血清中一邻位和二邻位氯取代的多氯联苯水平。其中一些多氯联苯同系物的水平比共平面多氯联苯、多氯二苯并对二恶英和多氯二苯并呋喃高出三个数量级。我们使用多氯二苯并对二恶英和多氯二苯并呋喃的国际毒性当量因子(TEF)以及Safe提出的多氯联苯的TEF来计算2,3,7,8 - TCDD当量。四种多氯联苯(3,3',4,4',5 - ;2,3',4,4',5 - ;2,3,3',4,4'-;2,3,3',4,4',5 - )的贡献比2,3,7,8 - TCDD更大,而其他四种多氯联苯(3,3',4,4'5,5'-;2,2',3,4,4',5'-;2,2',4,4',5,5'-;2,2',3,4,4',5,5'-)的贡献与2,3,7,8 - TCDD几乎相同。然而,在美国、瑞典和日本的一般人群样本中,单邻位氯取代的2,3',4,4',5 - PCB是总2,3,7,8 - TCDD当量的主要贡献者。(摘要截短于250字)