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牙科领域中潜在的空气传播石棉暴露:全面综述与风险评估。

Potential airborne asbestos exposures in dentistry: a comprehensive review and risk assessment.

机构信息

Cardno ChemRisk, Brooklyn, NY, USA.

Cardno ChemRisk, Arlington, VA, USA.

出版信息

Crit Rev Toxicol. 2021 Apr;51(4):301-327. doi: 10.1080/10408444.2021.1910624. Epub 2021 Jun 1.

Abstract

Chrysotile was formerly used in the manufacture of casting ring liner (CRL) and periodontal dressing powder (PDP). The purpose of this study was to describe the potential for airborne asbestos exposure among dental professionals who may have used these products and to assess their risk of asbestos-related disease (ARD). Task-specific exposure data associated with CRL and PDP were identified and compared to regulatory standards for asbestos and health-based benchmarks. Personal airborne fiber concentrations ranged from 0.008-3.5 f/cc by PCM (duration: 3-420 minutes) for CRL (tearing, placement), and from <0.0044-<0.297 f/cc by PCM (duration: 5-28 minutes) for PDP (mixing). Eight-hour time-weighted average (TWA) exposures were calculated using the reported task-based airborne fiber concentrations and associated sampling durations. For CRL tasks, the upper-bound calculated 8-hour TWA of 0.022 f/cc (tearing, placement) did not exceed regulatory standards for asbestos (≥0.1 f/cc). All samples collected during the mixing of PDP resulted in non-measurable fiber concentrations. The greatest estimated cumulative asbestos exposure for dental professionals using CRL (tearing, placement) of 0.33 f/cc-years is well below "best estimate", published chrysotile no-observed-adverse-effect-levels (NOAEL) for ARD (lung cancer = 89-168 f/cc-years; pleural mesothelioma = 208-415 f/cc-years). As such, the use of asbestos-containing CRL and/or PDP is not expected to pose an increased risk of ARD among dental professionals. This conclusion is consistent with the lack of an increased risk of ARD reported in epidemiological studies of these occupations.

摘要

温石棉曾用于铸造圈衬(CRL)和牙周敷料粉(PDP)的制造。本研究旨在描述曾使用过这些产品的牙科专业人员可能面临的空气中石棉暴露的潜在风险,并评估他们患与石棉相关的疾病(ARD)的风险。确定了与 CRL 和 PDP 相关的特定任务暴露数据,并将其与石棉监管标准和基于健康的基准进行了比较。通过 PCM(持续时间:3-420 分钟)测量,CRL(撕裂、放置)的个人空气中纤维浓度范围为 0.008-3.5 f/cc,通过 PCM(持续时间:5-28 分钟)测量,PDP(混合)的个人空气中纤维浓度范围为 <0.0044-<0.297 f/cc。使用报告的基于任务的空气中纤维浓度和相关采样持续时间计算 8 小时时间加权平均值(TWA)暴露。对于 CRL 任务,计算得出的 8 小时 TWA 上限值 0.022 f/cc(撕裂、放置)未超过石棉的监管标准(≥0.1 f/cc)。在 PDP 混合过程中收集的所有样本均导致纤维浓度不可测量。牙科专业人员使用 CRL(撕裂、放置)的估计累积石棉暴露量最高值为 0.33 f/cc 年,远低于“最佳估计”的、针对 ARD(肺癌=89-168 f/cc 年;胸膜间皮瘤=208-415 f/cc 年)发布的温石棉无观察到不良效应水平(NOAEL)。因此,预计在牙科专业人员中,使用含石棉的 CRL 和/或 PDP 不会增加患 ARD 的风险。这一结论与这些职业的流行病学研究报告的 ARD 风险未增加一致。

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