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BEI's in the Occupational Exposure Evaluation to Chemicals

机译:BEI在化学品职业接触评估中

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The technological development usually reduces chemical concentration in work environment. Simultaneously we meet growing number of low or even trace concentration of extremely dangerous chemicals like carcinogens, mutagens and teratogens. When we found larger quantity of different chemicals in air in various concentrations reliable measurement and analytical process could be difficult. Even using advanced analytical methods and procedures doesn't guarantee reliable results. Generally problems may be caused in two ways: collecting samples techniques and analytical procedures. Two techniques are commonly used for collecting the harmful chemical samples: bag air samples (like Tedlar) or vapor passive dosimetry badges. Both could be analyzed and then the concentration could be calculated in a period of time from the moment the exposure and sample collection took place. Both type samples frequently are sensitive for external factors like other chemicals concentration in the air, temperature, luminance or UV radiation as examples only. Analytical procedures that are performed in the laboratories could eliminate some errors but very rarely most of them, especially when higher number of chemicals has been identified. In described situation the classic methods of the evaluation of worker exposure are not sufficient and may result significant errors in estimation of health effect of the exposure. The commonly accepted procedures of monitoring harmful chemicals in occupational environment focuses on the measurement of the chemical concentration in the air and is usually performed as the series of samples collections. In the result we could obtain the average concentration level. The described procedure is accepted and effective for the workplaces of stable or repetitive operation scheme but is unaccepted when the operation scheme is accidental. The alternative for the classic monitoring method seems to be BEI (Biological Exposure Indicator) monitoring. We could find a lot of examples of positive results of BEI's implementation to the monitoring of human exposure (Kneip 1988, Boogard 1995 and 1996). The goal of this study is to verify and validate possibilities of implementation of BEI's in the assessment of occupational exposure to aromatic hydrocarbons - BTX group in the multiple and different levels concentration of other chemicals. Benzene, well known BTX representative is listed as carcinogen and mutagen factor. Other BTX hydrocarbons have not been listed as human carcinogens, however all their harmful health effects are not definitively examined epidemiologicaly, and their late effects are really difficult to discover. The precise and reliable assessment of exposure to BTX is critically important in this context. The measurement of the BTX concentration in the air doesn't cover the dermal exposure health effects neither the possible ingestion that is common because of frequently meet poor hygienic conditions and custom at the workplaces associated with the low risk perception among workers.
机译:技术发展通常会降低工作环境中的化学物质浓度。同时,我们遇到越来越多的低浓度甚至痕量浓度的极危险化学品,例如致癌物,诱变剂和致畸物。当我们发现空气中各种浓度的大量不同化学品时,可靠的测量和分析过程可能会很困难。即使使用高级分析方法和程序也不能保证可靠的结果。通常,问题可能通过两种方式引起:收集样品技术和分析程序。通常使用两种技术来收集有害的化学样品:袋装空气样品(如Tedlar)或蒸气被动剂量法徽章。可以对两者进行分析,然后可以从发生暴露和收集样品的那一刻起计算出浓度。两种类型的样品经常对外部因素敏感,例如空气中的其他化学物质浓度,温度,亮度或紫外线辐射,仅作为示例。在实验室中执行的分析程序可以消除一些错误,但大多数错误很少发生,尤其是在已识别出更多化学药品的情况下。在所描述的情况下,评估工人暴露的经典方法还不够,可能会在估计暴露对健康的影响方面导致重大错误。在职业环境中监视有害化学物质的普遍接受的程序集中于对空气中化学物质浓度的测量,通常以一系列样品收集的形式进行。结果,我们可以获得平均浓度水平。所描述的程序对于稳定或重复的操作方案的工作场所是可接受的且有效的,但是在偶然的操作方案时是不可接受的。传统监测方法的替代方法似乎是BEI(生物暴露指标)监测。我们可以找到许多BEI实施对人类暴露监测的积极成果的例子(Kneip 1988,Boogard 1995和1996)。这项研究的目的是验证和验证实施BEI评估芳烃的职业暴露的可能性-BTX组在多种不同浓度的其他化学品中。苯(众所周知的BTX代表)被列为致癌物和诱变因子。其他BTX碳氢化合物尚未被列为人类致癌物,但是尚未对其流行病学进行彻底的健康检查,而且其后期影响确实很难发现。在这种情况下,准确可靠地评估BTX暴露至关重要。空气中BTX浓度的测量并未涵盖皮肤接触对健康的影响,也没有涵盖由于经常遇到不良的卫生条件和在工作场所习惯而导致的常见摄入,以及与工人之间低风险感相关的习惯。

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