铅的神经行为毒理学和畸形学。

G Winneke, H Lilienthal, U Krämer
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引用次数: 69

摘要

当比较来自职业性铅暴露的成年人和环境铅暴露的儿童的神经行为观察时,似乎发育中的大脑相对于成熟的大脑更危险。在血铅浓度低于400微克/升时,职业性铅暴露的神经行为毒性通常未被观察到,而在环境暴露的儿童中,这种缺陷已被报道发生在100-150微克/升,甚至可能低于这一范围。横断面研究和前瞻性研究在这方面都得出了类似的结论。在大多数这样的研究中,首选的终点是智商测量,它具有良好的心理测量质量,足够好地标准化,可以在不同的研究中进行比较,并且在公共卫生背景下,对监管者来说,表现出具有吸引力的简单性。然而,与此同时,这种对智商的关注也干扰了通过更详细的神经行为分析来识别更具体的铅诱发的功能缺陷的系统努力(Bellinger 1995)。对铅接触儿童的横断面研究和前瞻性研究的荟萃分析得出结论,多氯联苯从100微克/升增加一倍至200微克/升,与平均智商下降1-3分有关(Pocock等人,1994;世卫组织,1995年),尚未确定阈值。然而,由于在流行病学研究中,如果观察到的影响像这些一样微妙,因果关系必然仍然值得怀疑,因此,动物实验研究有助于支持铅在稳定状态PbB降至约150至200微克/升时产生神经行为缺陷的致病作用。这种缺陷已经在大鼠和灵长类动物中通过各种具有正强化和负强化偶发的学习/记忆模型得到了证明。这些研究也表明,在断奶后停止接触后,早期发育暴露后的神经行为缺陷会长期延续到成年期。因此,到目前为止,铅的神经行为致畸似乎在动物模型中比在人类接触条件下得到了更令人信服的证明。目前还缺乏一个连贯的理论来解释发育中的大脑对铅的特殊脆弱性。然而,最近的数据确实表明,铅引起的未成熟大脑中钙稳态的破坏可能会干扰正常的大脑发育。
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The neurobehavioural toxicology and teratology of lead.

When comparing neurobehavioural observations from occupational lead-exposure of adults on the one hand, and environmental lead exposure of children on the other, it appears that the developing relative to the mature brain is more at risk. Neurobehavioural toxicity in occupational lead-exposure has typically not been observed at blood lead-concentrations (PbBs) below 400 micrograms/l, whereas ih environmentally exposed children such deficit has been reported to occur down to PbB of 100-150 micrograms/l and, perhaps, even below this range. Both cross-sectional and prospective studies have arrived at similar conclusions in this respect. The preferred endpoint in most such studies has been the IQ-measure, which has good psychometric qualities, is sufficiently well standardized to be comparable across studies, and exhibits attractive simplicity for the regulator in a public health context. At the same time, however, this IQ-focus has also interfered with systematic efforts to identify more specific lead-induced functional deficits by means of more detailed neurobehavioural analyses (Bellinger 1995). Metanalyses on both cross sectional and prospective studies in lead-exposed children have concluded that a typical doubling of PbB from 100 to 200 micrograms/l is associated with an average IQ-loss of 1-3 points (Pocock et al. 1994; WHO 1995), and no threshold has as yet been identified. Since, however, cause-effect contingencies necessarily remain doubtful in epidemiological studies if the observed effects are as subtle as these, experimental studies in animals have become helpful in supporting the causative role of lead to produce neurobehavioural deficit at steady-state PbB down to about 150 to 200 micrograms/l. Such deficit has been demonstrated by means of a variety of learning/memory models with positive and negative reinforcement contingencies in the rat--and in primates as well. It has also been shown in such studies that neurobehavioural deficit subsequent to early developmental exposure extends long into adulthood after cessation of exposure at weaning. It, therefore, appears that the neurobehavioural teratology of lead has more convincingly been demonstrated in animal models than in human exposure conditions, so far. A coherent theory to explain the particular vulnerability to lead of the developing brain is still lacking. Recent data do suggest, however, that Pb-induced disruption of calcium homeostasis in the immature brain might interfere with normal brain development.

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