Munro N B, Talmage S S, Griffin G D, Waters L C, Watson A P, King J F, Hauschild V
Life Sciences Division, Oak Ridge National Laboratory, Oak Ridge, TN 37830, USA.
Environ Health Perspect. 1999 Dec;107(12):933-74. doi: 10.1289/ehp.99107933.
We include in this review an assessment of the formation, environmental fate, and mammalian and ecotoxicity of CW agent degradation products relevant to environmental and occupational health. These parent CW agents include several vesicants: sulfur mustards [undistilled sulfur mustard (H), sulfur mustard (HD), and an HD/agent T mixture (HT)]; nitrogen mustards [ethylbis(2-chloroethyl)amine (HN1), methylbis(2-chloroethyl)amine (HN2), tris(2-chloroethyl)amine (HN3)], and Lewisite; four nerve agents (O-ethyl S-[2-(diisopropylamino)ethyl] methylphosphonothioate (VX), tabun (GA), sarin (GB), and soman (GD)); and the blood agent cyanogen chloride. The degradation processes considered here include hydrolysis, microbial degradation, oxidation, and photolysis. We also briefly address decontamination but not combustion processes. Because CW agents are generally not considered very persistent, certain degradation products of significant persistence, even those that are not particularly toxic, may indicate previous CW agent presence or that degradation has occurred. Of those products for which there are data on both environmental fate and toxicity, only a few are both environmentally persistent and highly toxic. Major degradation products estimated to be of significant persistence (weeks to years) include thiodiglycol for HD; Lewisite oxide for Lewisite; and ethyl methyl phosphonic acid, methyl phosphonic acid, and possibly S-(2-diisopropylaminoethyl) methylphosphonothioic acid (EA 2192) for VX. Methyl phosphonic acid is also the ultimate hydrolysis product of both GB and GD. The GB product, isopropyl methylphosphonic acid, and a closely related contaminant of GB, diisopropyl methylphosphonate, are also persistent. Of all of these compounds, only Lewisite oxide and EA 2192 possess high mammalian toxicity. Unlike other CW agents, sulfur mustard agents (e.g., HD) are somewhat persistent; therefore, sites or conditions involving potential HD contamination should include an evaluation of both the agent and thiodiglycol.
我们在本综述中纳入了对与环境和职业健康相关的化学战剂降解产物的形成、环境归宿以及对哺乳动物和生态毒性的评估。这些化学战剂母体包括几种糜烂性毒剂:硫芥(未蒸馏硫芥(H)、硫芥(HD)以及HD/芥子气T混合物(HT));氮芥(乙基双(2-氯乙基)胺(HN1)、甲基双(2-氯乙基)胺(HN2)、三(2-氯乙基)胺(HN3))以及路易氏剂;四种神经性毒剂(O-乙基-S-[2-(二异丙氨基)乙基]甲基硫代膦酸酯(VX)、塔崩(GA)、沙林(GB)以及梭曼(GD));以及血液毒剂氯化氰。这里所考虑的降解过程包括水解、微生物降解、氧化和光解。我们还简要讨论了去污但未涉及燃烧过程。由于化学战剂通常不被认为具有很强的持久性,某些具有显著持久性的降解产物,即使那些毒性不是特别大的,也可能表明之前存在化学战剂或已经发生了降解。在那些既有环境归宿数据又有毒性数据的产物中,只有少数几种在环境中具有持久性且毒性很高。估计具有显著持久性(数周至数年)的主要降解产物包括HD的硫二甘醇;路易氏剂的路易氏剂氧化物;以及VX的乙基甲基膦酸、甲基膦酸以及可能的S-(2-二异丙氨基乙基)甲基硫代膦酸(EA 2192)。甲基膦酸也是GB和GD的最终水解产物。GB的产物异丙基甲基膦酸以及GB的一种密切相关污染物二异丙基甲基膦酸酯也具有持久性。在所有这些化合物中,只有路易氏剂氧化物和EA 2192具有高哺乳动物毒性。与其他化学战剂不同,硫芥制剂(如HD)具有一定的持久性;因此,涉及潜在HD污染的场所或条件应包括对该制剂和硫二甘醇的评估。