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The Concept of 'Practical Thresholds' in the Derivation of Occupational Exposure Limits for Carcinogens by the Scientic Committee on Occupational Exposure Limits (SCOEL) of the European Union

机译:欧盟职业接触限值科学委员会(SCOEL)在推导致癌物职业接触限值中的“实用阈值”概念

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In Europe, there has been a scientic discussion on possible thresholds in chemical carcinogens since the late 1990s. Based on this discussion, the Scientic Committee on Occupational Exposure Limits (SCOEL) of the European Union has discussed a number of chemical carcinogens and has issued recommendations. For some carcinogens, health-based Occupational Exposure Limits (OELs) were recommended, while quantitative assessments of carcinogenic risks were performed for others. For purposes of setting OELs the following groups of carcinogens were adopted: (A) Non-threshold genotoxic carcinogens; for low-dose assessment of risk, the linear non-threshold (LNT) model appears appropriate. For these chemicals, the risk management may be based on the ALARA principle ("as low as reasonably achievable"), technical feasibility, and other socio-political considerations. (B) Genotoxic carcinogens, for which the existence of a threshold cannot be su?ciently supported at present. In these cases, the LNT model may be used as a default assumption, based on the scientic uncertainty, and the ALARA principle may be applied as well. (C) Genotoxic carcinogens with a practical threshold is supported by studies on mechanisms and/or toxicokinetics; health-based exposure limits may be based on an established no-observed adverse esect level (NOAEL). (D) Non-genotoxic carcinogens and non DNAreactive carcinogens; for these compounds a true ("perfect") threshold is associated with a clearly founded NOAEL. The mechanisms shown by tumor promoters, spindle poisons, topoisomerase II poisons and hormones are typical examples of this category. Health-based OELs are derived for carcinogens of Groups C and D, while a risk assessment is carried out for carcinogens of Groups A and B. In order to highlight the most important diserentiation between Groups B and C, the basic reasoning is given for the six compounds formaldehyde, vinyl acetate, acrylonitrile, acrylamide, trichloroethylene and methylene chloride.
机译:自1990年代后期以来,在欧洲就化学致癌物的可能阈值进行了科学讨论。在此讨论的基础上,欧洲联盟职业接触限值科学委员会(SCOEL)讨论了许多化学致癌物并提出了建议。对于某些致癌物,建议采用基于健康的职业接触限值(OELs),而对其他致癌物则进行定量评估。为了设定OEL,采用了以下几类致癌物:(A)非阈值遗传毒性致癌物;对于低剂量风险评估,线性非阈值(LNT)模型似乎很合适。对于这些化学品,风险管理可以基于ALARA原则(“尽可能合理地降低”),技术可行性和其他社会政治因素。 (B)基因毒性致癌物,目前尚不能充分支持其阈值的存在。在这种情况下,基于科学的不确定性,可以将LNT模型用作默认假设,也可以应用ALARA原理。 (C)对机理和/或毒物动力学的研究支持了具有实际阈值的遗传毒性致癌物;基于健康的接触限值可以基于已建立的未观察到的有害菌水平(NOAEL)。 (D)非遗传毒性致癌物和非DNA反应性致癌物;对于这些化合物,真正的(“完美”)阈值与明确建立的NOAEL有关。肿瘤启动子,纺锤体毒物,拓扑异构酶II毒物和激素所显示的机制是此类的典型例子。基于健康的OEL是针对C和D组的致癌物而衍生的,而风险评估是针对A和B组的致癌物进行的。为了突出B和C组之间最重要的区别,给出了六种化合物:甲醛,乙酸乙烯酯,丙烯腈,丙烯酰胺,三氯乙烯和二氯甲烷。

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