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本文引用的文献

1
Analysis of human milk to assess exposure to PAHs, PCBs and organochlorine pesticides in the vicinity Mediterranean city Mersin, Turkey.分析人乳以评估土耳其地中海城市梅尔辛附近多环芳烃、多氯联苯和有机氯农药的暴露情况。
Environ Int. 2012 Apr;40:63-69. doi: 10.1016/j.envint.2011.11.012. Epub 2011 Dec 31.
2
Concentrations of polychlorinated dibenzo-p-dioxins, polychlorinated dibenzofurans, and polychlorinated biphenyls in blood and breast milk collected from pregnant women in Sapporo City, Japan.日本札幌市孕妇血液和母乳中多氯二苯并对二恶英、多氯二苯并呋喃和多氯联苯的浓度。
Chemosphere. 2011 Dec;85(11):1694-700. doi: 10.1016/j.chemosphere.2011.09.014. Epub 2011 Oct 17.
3
Neurotoxic effects in adult mice neonatally exposed to 3,3'4,4'5-pentachlorobiphenyl or 2,3,3'4,4'-pentachlorobiphenyl. Changes in brain nicotinic receptors and behaviour.新生期暴露于 3,3'4,4'5-五氯联苯或 2,3,3'4,4'-五氯联苯的成年小鼠的神经毒性作用。大脑烟碱受体和行为的变化。
Environ Toxicol Pharmacol. 1998 Jan;5(1):17-27. doi: 10.1016/s1382-6689(97)10002-3.
4
In utero and lactational exposure to PCBs in mice: adult offspring show altered learning and memory depending on Cyp1a2 and Ahr genotypes.在子宫内和哺乳期暴露于 PCBs 会对老鼠造成影响:成年后代的学习和记忆会发生改变,这取决于 Cyp1a2 和 Ahr 基因型。
Environ Health Perspect. 2011 Sep;119(9):1286-93. doi: 10.1289/ehp.1002965. Epub 2011 May 13.
5
Investigating intergenerational differences in human PCB exposure due to variable emissions and reproductive behaviors.研究由于排放和生殖行为的变化而导致人类 PCB 暴露在代际差异中的情况。
Environ Health Perspect. 2011 May;119(5):641-6. doi: 10.1289/ehp.1002415. Epub 2010 Dec 14.
6
In utero and lactational exposure to a complex mixture of polychlorinated biphenyls: toxicity in pups dependent on the Cyp1a2 and Ahr genotypes.子宫内和哺乳期暴露于多氯联苯的复杂混合物中:Cyp1a2 和 Ahr 基因型依赖性幼仔的毒性。
Toxicol Sci. 2011 Jan;119(1):189-208. doi: 10.1093/toxsci/kfq314. Epub 2010 Oct 20.
7
Developmental PCB exposure induces hypothyroxinemia and sex-specific effects on cerebellum glial protein levels in rats.发育期接触多氯联苯会导致大鼠甲状腺素水平过低,并对其小脑神经胶质蛋白水平产生性别特异性影响。
Int J Dev Neurosci. 2010 Nov;28(7):553-60. doi: 10.1016/j.ijdevneu.2010.07.237. Epub 2010 Aug 5.
8
A common carcinogen benzo[a]pyrene causes neuronal death in mouse via microglial activation.一种常见的致癌物质苯并[a]芘通过小胶质细胞的激活导致小鼠神经元死亡。
PLoS One. 2010 Apr 1;5(4):e9984. doi: 10.1371/journal.pone.0009984.
9
Estimating the half-lives of PCB congeners in former capacitor workers measured over a 28-year interval.估算电容器工人在 28 年时间跨度内测量的多氯联苯同系物的半衰期。
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10
Occupational exposure to PCBs reduces striatal dopamine transporter densities only in women: a beta-CIT imaging study.职业性接触多氯联苯仅降低女性纹状体多巴胺转运蛋白密度:一项β-CIT 成像研究。
Neurobiol Dis. 2010 May;38(2):219-25. doi: 10.1016/j.nbd.2010.01.009. Epub 2010 Jan 20.

Ahrd Cyp1a2(-/-) 小鼠对 PCB 诱导的发育性神经毒性的易感性增加。

Ahrd Cyp1a2(-/-) mice show increased susceptibility to PCB-induced developmental neurotoxicity.

机构信息

Department of Biological Sciences, Northern Kentucky University, Highland Heights, KY, USA.

Department of Biological Sciences, Northern Kentucky University, Highland Heights, KY, USA.

出版信息

Neurotoxicology. 2012 Dec;33(6):1436-1442. doi: 10.1016/j.neuro.2012.08.005. Epub 2012 Aug 23.

DOI:10.1016/j.neuro.2012.08.005
PMID:22935098
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC3518762/
Abstract

Polychlorinated biphenyls (PCBs) are developmental neurotoxicants that produce cognitive and behavioral changes in children exposed during gestation and lactation. Coplanar PCBs bind the aryl hydrocarbon receptor (AHR) and can be sequestered in liver by cytochrome P450 1A2 (CYP1A2). The AHR is a ligand-activated transcription factor which increases expression of the CYP1 family, including CYP1A2. Our previous work examining genetic susceptibility to developmental PCB neurotoxicity showed that Ahr(b)Cyp1a2(-/-) mice with the high-affinity Ahr(b) allele and lacking CYP1A2 were most susceptible while Ahr(b)Cyp1a2(+/+) and poor-affinity Ahr(d)Cyp1a2(+/+) mice were resistant. To follow up, a fourth line of mice was generated with the Ahr(d)Cyp1a2(-/-) genotype and compared with the background strain Ahr(b)Cyp1a2(+/+). Dams received a PCB mixture or the corn oil vehicle at gestational Day 10 (GD10) and postnatal Day 5 (PND5). Offspring were tested at PND60 in open field locomotor, acoustic startle with pre-pulse inhibition (PPI), novel object recognition and Morris water maze. Locomotor activity was increased in PCB-treated Ahr(b)Cyp1a2(+/+) mice, but no differences were seen in control vs. PCB-treated Ahr(d)Cyp1a2(-/-) mice. PCB-treated Ahr(d)Cyp1a2(-/-) mice had a higher baseline startle response and significantly reduced pre-pulse inhibition at the 74dB level compared with corn oil-treated controls (P<0.05). PCB-treated Ahr(d)Cyp1a2(-/-) mice had impairments in novel objective recognition (P<0.05) and during all three hidden platform phases of Morris water maze (P<0.01). Combined with our previous findings, these results indicate Cyp1a2 genotype is more important in susceptibility to PCB-induced deficits in learning and memory, but Ahr genotype appears more important when assessing acoustic startle-PPI and locomotor activity.

摘要

多氯联苯(PCBs)是发育神经毒物,会导致暴露于妊娠期和哺乳期的儿童认知和行为改变。共平面 PCB 结合芳香烃受体(AHR),并可被细胞色素 P450 1A2(CYP1A2)隔离在肝脏中。AHR 是一种配体激活的转录因子,可增加 CYP1 家族的表达,包括 CYP1A2。我们之前研究遗传易感性对发育性 PCB 神经毒性的影响发现,具有高亲和力 Ahr(b)等位基因且缺乏 CYP1A2 的 Ahr(b)Cyp1a2(-/-)小鼠最易受影响,而 Ahr(b)Cyp1a2(+/+)和低亲和力 Ahr(d)Cyp1a2(+/+)小鼠则具有抗性。为了跟进,我们生成了第四种带有 Ahr(d)Cyp1a2(-/-)基因型的小鼠,并与背景品系 Ahr(b)Cyp1a2(+/+)进行了比较。母鼠在妊娠第 10 天(GD10)和出生后第 5 天(PND5)接受 PCB 混合物或玉米油处理。后代在 PND60 时进行了旷场运动、带有预脉冲抑制的听觉惊跳反应、新物体识别和 Morris 水迷宫测试。在 PCB 处理的 Ahr(b)Cyp1a2(+/+)小鼠中,运动活性增加,但在对照与 PCB 处理的 Ahr(d)Cyp1a2(-/-)小鼠之间未观察到差异。与玉米油处理的对照组相比,PCB 处理的 Ahr(d)Cyp1a2(-/-)小鼠的基础惊跳反应更高,在 74dB 水平的预脉冲抑制显著降低(P<0.05)。PCB 处理的 Ahr(d)Cyp1a2(-/-)小鼠在新物体识别(P<0.05)和 Morris 水迷宫的所有三个隐藏平台阶段中都存在学习和记忆缺陷(P<0.01)。结合我们之前的发现,这些结果表明 CYP1A2 基因型在易感性方面更为重要,而在评估听觉惊跳反应-PPI 和运动活性时,AHR 基因型似乎更为重要。