Bridges Jim, Solomon Keith R
a Department of Toxicology and Environmental Health , University of Surrey , Guildford , Surrey , United Kingdom.
b Centre for Toxicology, School of Environmental Sciences , University of Guelph , Guelph , Ontario , Canada.
J Toxicol Environ Health B Crit Rev. 2016;19(8):345-379. doi: 10.1080/10937404.2016.1200505. Epub 2016 Sep 22.
Cyclic volatile methyl siloxanes (cVMSs) are highly volatile and have an unusual combination of physicochemical properties, which are unlike those of halocarbon-based chemicals used to establish criteria for identification of persistent organic pollutants (POPs) that undergo long-range transport (LRT). A transparent quantitative weight of evidence (QWoE) evaluation was conducted to characterize their properties. Measurements of concentrations of cVMSs in the environment are challenging, but currently, concentrations measured in robust studies are all less than thresholds of toxicity. The cVMSs are moderately persistent in air with half-lives ≤11 d (greater than the criterion of 2 d) but these compounds partition into the atmosphere, the final sink. The cVMSs are rapidly degraded in dry soils, partition from wet soils into the atmosphere, and are not classifiable as persistent in soils. Persistence in water and sediment is variable, but the greatest concentrations in the environment are observed in sediments. Based upon the measurements that have been made in the environment, cVMSs should not be classified as persistent. Studies in food webs support a conclusion that the cVMSs do not biomagnify, a conclusion that is consistent with results of toxicokinetic studies. Concentrations in air in remote locations are small and deposition has not been detected. Taken together, evidence indicates that traditional measures of persistence and biomagnification used for legacy POP are not suitable for cVMS. Refined approaches used here suggest that cVMSs are not classifiable as persistent, bioaccumulative, or toxic. Further, these chemicals do not undergo LRT in the sense of legacy POPs.
环状挥发性甲基硅氧烷(cVMSs)具有高挥发性,其理化性质组合独特,与用于确定经历长距离传输(LRT)的持久性有机污染物(POPs)标准的卤代烃类化学品不同。开展了一项透明的定量证据权重(QWoE)评估以表征其性质。测量环境中cVMSs的浓度具有挑战性,但目前,在可靠研究中测得的浓度均低于毒性阈值。cVMSs在空气中具有一定持久性,半衰期≤11天(大于2天的标准),但这些化合物会分配到大气这个最终汇中。cVMSs在干燥土壤中迅速降解,从潮湿土壤中分配到大气中,在土壤中不能归类为持久性物质。在水中和沉积物中的持久性各不相同,但在环境中观察到的最高浓度出现在沉积物中。基于在环境中所做的测量,cVMSs不应被归类为持久性物质。食物网研究支持cVMSs不会发生生物放大的结论,这一结论与毒代动力学研究结果一致。偏远地区空气中的浓度很低,尚未检测到沉降。综合来看,有证据表明用于传统POPs的持久性和生物放大的传统衡量标准不适用于cVMSs。此处使用的精细方法表明,cVMSs不能归类为持久性、生物累积性或有毒物质。此外,从传统POPs的意义上讲,这些化学品不会经历长距离传输。