Bernstein David M, Hoskins John A
Regul Toxicol Pharmacol. 2006 Aug;45(3):252-64. doi: 10.1016/j.yrtph.2006.04.008. Epub 2006 Jul 11.
This review substantiates kinetically and pathologically the differences between chrysotile and amphiboles. The serpentine chrysotile is a thin walled sheet silicate while the amphiboles are double-chain silicates. These different chemistries result in chrysotile clearing very rapidly from the lung (T(1/2)=0.3 to 11 days) while amphiboles are among the slowest clearing fibers known (T(1/2)=500 days to infinity). Across the range of mineral fiber solubilities chrysotile lies towards the soluble end of the scale. Chronic inhalation toxicity studies with chrysotile in animals have unfortunately been performed at very high exposure concentrations resulting in lung overload. Consequently their relevance to human exposures is extremely limited. Chrysotile following subchronic inhalation at a mean exposure of 76 fibers L>20 microm/cm(3) (3413 total fibers/cm(3)) resulted in no fibrosis (Wagner score 1.8-2.6), at any time point and no difference with controls in BrdU response or biochemical and cellular parameters. The long chrysotile fibers were observed to break apart into small particles and smaller fibers. Toxicologically, chrysotile which rapidly falls apart in the lung behaves more like non-fibrous mineral dusts while response to amphibole asbestos reflects its insoluble fibrous structure. Recent quantitative reviews of epidemiological studies of mineral fibers have determined the potency of chrysotile and amphibole asbestos for causing lung cancer and mesothelioma in relation to fiber type have also differentiated between these two minerals. The most recent analyses also concluded that it is the longer, thinner fibers that have the greatest potency as has been reported in animal inhalation toxicology studies. However, one of the major difficulties in interpreting these studies is that the original exposure estimates rarely differentiated between chrysotile and amphiboles. Not unlike some other respirable particulates, to which humans are, or have been heavily occupationally exposed, there is evidence that heavy and prolonged exposure to chrysotile can produce lung cancer. The value of the present and other similar studies is that they show that low exposures to pure chrysotile do not present a detectable risk to health. Since total dose over time decides the likelihood of disease occurrence and progression, they also suggest that the risk of an adverse outcome may be low if even any high exposures experienced were of short duration.
这篇综述从动力学和病理学角度证实了温石棉和闪石之间的差异。蛇纹石类的温石棉是一种薄壁片状硅酸盐,而闪石是双链硅酸盐。这些不同的化学组成导致温石棉在肺部清除速度非常快(半衰期T(1/2)=0.3至11天),而闪石是已知清除最慢的纤维之一(半衰期T(1/2)=500天至无限长)。在矿物纤维溶解度范围内,温石棉处于可溶端。不幸的是,在动物身上进行的温石棉慢性吸入毒性研究是在非常高的暴露浓度下进行的,导致肺部负荷过重。因此,它们与人类暴露的相关性极为有限。在平均暴露量为76根纤维/L>20微米/立方厘米(3413根总纤维/立方厘米)的情况下进行亚慢性吸入后,温石棉在任何时间点都未导致纤维化(瓦格纳评分1.8 - 2.6),且在BrdU反应或生化及细胞参数方面与对照组无差异。观察到长的温石棉纤维会断裂成小颗粒和更细的纤维。从毒理学角度来看,在肺部迅速分解的温石棉表现得更像非纤维状矿物粉尘,而对闪石石棉的反应则反映了其不溶性纤维结构。近期对矿物纤维流行病学研究的定量综述确定了温石棉和闪石石棉导致肺癌和间皮瘤的效力,也区分了这两种矿物。最新分析还得出结论,正如动物吸入毒理学研究所报道的那样,较长、较细的纤维效力最大。然而,解释这些研究的一个主要困难在于,最初的暴露估计很少区分温石棉和闪石。与人类大量或曾经大量职业暴露的其他一些可吸入颗粒物并无不同,有证据表明,大量且长期暴露于温石棉会引发肺癌。当前及其他类似研究的价值在于,它们表明低剂量暴露于纯温石棉不会对健康构成可检测到的风险。由于随时间累积的总剂量决定了疾病发生和进展的可能性,它们还表明,如果即使是任何高剂量暴露的持续时间很短,不良后果的风险可能也很低。