瑞典硬质金属工业中钴和钨的职业暴露:颗粒质量、数量和表面积的空气浓度。

Annals of Occupational Hygiene Pub Date : 2016-07-01 Epub Date: 2016-05-03 DOI:10.1093/annhyg/mew023
Maria Klasson, Ing-Liss Bryngelsson, Carin Pettersson, Bente Husby, Helena Arvidsson, Håkan Westberg
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引用次数: 42

摘要

在硬金属工业中接触钴会对健康造成严重的不利影响,包括肺癌和硬金属纤维化。本研究的主要目的是确定钴和钨的暴露空气浓度水平,以便在我们对瑞典一家硬金属厂的医学调查中进行风险评估和剂量反应分析。我们还介绍了固定采样的质量基础、颗粒表面积和颗粒数空气浓度,并研究了在我们的研究中使用这些数据作为暴露测量的代理的可能性。对可吸入粉尘和总粉尘、钴和钨进行个人暴露全位移测量,包括个人实时连续监测粉尘。还进行了可吸入粉尘和总粉尘、PM2.5和PM10的固定测量,并确定了钴和钨的水平,以及空气中颗粒数的浓度和细颗粒的颗粒表面积。个人可吸入粉尘暴露水平持续较低(AM 0.15mg m(-3),范围
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Occupational Exposure to Cobalt and Tungsten in the Swedish Hard Metal Industry: Air Concentrations of Particle Mass, Number, and Surface Area.

Occupational Exposure to Cobalt and Tungsten in the Swedish Hard Metal Industry: Air Concentrations of Particle Mass, Number, and Surface Area.

Occupational Exposure to Cobalt and Tungsten in the Swedish Hard Metal Industry: Air Concentrations of Particle Mass, Number, and Surface Area.

Occupational Exposure to Cobalt and Tungsten in the Swedish Hard Metal Industry: Air Concentrations of Particle Mass, Number, and Surface Area.

Exposure to cobalt in the hard metal industry entails severe adverse health effects, including lung cancer and hard metal fibrosis. The main aim of this study was to determine exposure air concentration levels of cobalt and tungsten for risk assessment and dose-response analysis in our medical investigations in a Swedish hard metal plant. We also present mass-based, particle surface area, and particle number air concentrations from stationary sampling and investigate the possibility of using these data as proxies for exposure measures in our study. Personal exposure full-shift measurements were performed for inhalable and total dust, cobalt, and tungsten, including personal real-time continuous monitoring of dust. Stationary measurements of inhalable and total dust, PM2.5, and PM10 was also performed and cobalt and tungsten levels were determined, as were air concentration of particle number and particle surface area of fine particles. The personal exposure levels of inhalable dust were consistently low (AM 0.15mg m(-3), range <0.023-3.0mg m(-3)) and below the present Swedish occupational exposure limit (OEL) of 10mg m(-3) The cobalt levels were low as well (AM 0.0030mg m(-3), range 0.000028-0.056mg m(-3)) and only 6% of the samples exceeded the Swedish OEL of 0.02mg m(-3) For continuous personal monitoring of dust exposure, the peaks ranged from 0.001 to 83mg m(-3) by work task. Stationary measurements showed lower average levels both for inhalable and total dust and cobalt. The particle number concentration of fine particles (AM 3000 p·cm(-3)) showed the highest levels at the departments of powder production, pressing and storage, and for the particle surface area concentrations (AM 7.6 µm(2)·cm(-3)) similar results were found. Correlating cobalt mass-based exposure measurements to cobalt stationary mass-based, particle area, and particle number concentrations by rank and department showed significant correlations for all measures except for particle number. Linear regression analysis of the same data showed statistically significant regression coefficients only for the mass-based aerosol measures. Similar results were seen for rank correlation in the stationary rig, and linear regression analysis implied significant correlation for mass-based and particle surface area measures. The mass-based air concentration levels of cobalt and tungsten in the hard metal plant in our study were low compared to Swedish OELs. Particle number and particle surface area concentrations were in the same order of magnitude as for other industrial settings. Regression analysis implied the use of stationary determined mass-based and particle surface area aerosol concentration as proxies for various exposure measures in our study.

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