Murbach Dana M, Madl Amy K, Unice Ken M, Knutsen Jeffrey S, Chapman Pamela S, Brown Jay L, Paustenbach Dennis J
ChemRisk, 25 Jessie Street, Suite 1800, San Francisco, CA 94105, USA.
Ann Occup Hyg. 2008 Jun;52(4):267-79. doi: 10.1093/annhyg/men015. Epub 2008 May 8.
The exposure of shipyard workers to asbestos has been frequently investigated during the installation, repair or removal of asbestos insulation. The same level of attention, however, has not been directed to asbestos exposure of maritime seamen or sailors. In this paper, we assemble and analyze historical industrial hygiene (IH) data quantifying airborne asbestos concentrations onboard maritime shipping vessels between 1978 and 1992. Air monitoring and bulk sampling data were compiled from 52 IH surveys conducted on 84 different vessels, including oil tankers and cargo vessels, that were docked and/or at sea, but these were not collected during times when there was interaction with asbestos-containing materials (ACMs). One thousand and eighteen area air samples, 20 personal air samples and 24 air samples of unknown origin were analyzed by phase contrast microscopy (PCM); 19 area samples and six samples of unknown origin were analyzed by transmission electron microscopy (TEM) and 13 area air samples were analyzed by scanning electron microscopy (SEM). In addition, 482 bulk samples were collected from suspected ACMs, including insulation, ceiling panels, floor tiles, valve packing and gaskets. Fifty-three percent of all PCM and 4% of all TEM samples were above their respective detection limits. The average airborne concentration for the PCM area samples (n = 1018) was 0.008 fibers per cubic centimeter (f cc(-1)) (95th percentile of 0.040 f cc(-1)). Air concentrations in the living and recreational areas of the vessels (e.g. crew quarters, common rooms) averaged 0.004 f cc(-1) (95th percentile of 0.014 f cc(-1)), while air concentrations in the engine rooms and machine shops averaged 0.010 f cc(-1) (95th percentile of 0.068 f cc(-1)). Airborne asbestos concentrations were also classified by vessel type (cargo, tanker or Great Lakes), transport status (docked or underway on active voyage) and confirmed presence of ACM. Approximately 1.3 and 0% of the 1018 area samples analyzed by PCM exceeded 0.1 and 1 f cc(-1), respectively. This data set indicates that historic airborne asbestos concentrations on these maritime shipping vessels, when insulation-handling activities were not actively being performed, were consistently below contemporaneous US occupational standards from 1978 until 1992, and nearly always below the current permissible exposure limit of 0.1 f cc(-1).
在安装、维修或拆除石棉绝缘材料的过程中,造船厂工人接触石棉的情况经常受到调查。然而,对于海员或水手接触石棉的关注程度却没有达到同样的水平。在本文中,我们收集并分析了1978年至1992年间量化海上船舶空气中石棉浓度的历史工业卫生(IH)数据。空气监测和散装采样数据来自对84艘不同船舶(包括油轮和货船)进行的52次IH调查,这些船舶停靠在码头和/或处于海上,但这些数据并非在与含石棉材料(ACM)有交互作用期间收集的。通过相差显微镜(PCM)分析了1018个区域空气样本、20个个人空气样本和24个来源不明的空气样本;通过透射电子显微镜(TEM)分析了19个区域样本和6个来源不明的样本,通过扫描电子显微镜(SEM)分析了13个区域空气样本。此外,从疑似ACM中收集了482个散装样本,包括绝缘材料、天花板面板、地砖、阀门填料和垫圈。所有PCM样本的53%和所有TEM样本的4%超过了各自的检测限。PCM区域样本(n = 1018)的平均空气传播浓度为每立方厘米0.008纤维(f cc(-1))(第95百分位数为0.040 f cc(-1))。船舶生活和娱乐区域(如船员宿舍、公共活动室)的空气浓度平均为0.004 f cc(-1)(第95百分位数为0.014 f cc(-1)),而机舱和机械车间的空气浓度平均为0.010 f cc(-1)(第95百分位数为0.068 f cc(-1))。空气中石棉浓度还按船舶类型(货船、油轮或五大湖船舶)、运输状态(停靠或在航行中)以及确认存在ACM进行分类。通过PCM分析的1018个区域样本中,分别约有1.3%和0%超过了0.1和1 f cc(-1)。该数据集表明,在这些海上船舶上,当绝缘材料处理活动未积极进行时,1978年至1992年期间空气中石棉的历史浓度始终低于同期美国职业标准,并且几乎总是低于当前0.1 f cc(-1)的允许接触限值。