Webber J S, Syrotynski S, King M V
Wadsworth Center for Laboratories and Research, New York State Department of Health, Albany 12201-0509.
Environ Res. 1988 Aug;46(2):153-67. doi: 10.1016/s0013-9351(88)80029-x.
Asbestos contamination in excess of 10 billion fibers per liter was detected in a community's drinking water. To assess the possibility of waterborne asbestos becoming airborne, air samples were collected from impacted houses receiving contaminated water from three control houses. Collected within each house were three samples on 0.6-micrometer-pore Nuclepore filters and three samples on 0.8-micrometer-pore Millipore filters. In addition, bulk samples of suspect material and water samples were collected. Mean waterborne asbestos concentrations were 24 million fibers per liter (MFL) in the impacted houses versus only 1.1 MFL in the control houses. Transmission electron microscopy revealed that airborne asbestos concentrations were highest in impacted houses, with airborne asbestos concentrations positively correlated with waterborne concentrations. For fiber and mass measurements on both filter types, airborne asbestos concentrations were significantly higher in the impacted houses: mean concentrations in impacted houses were 0.12 fibers/cm3 and 1.7 ng/m3 on Nuclepore filters and 0.053 fibers/cm3 and 2.3 ng/m3 on Millipore filters versus only 0.037 fibers/cm3 and 0.31 ng/m3 on Nuclepore filters and 0.0077 fibers/cm3 and 0.14 ng/m3 on Millipore filters from control houses. Also detected in the air samples from impacted houses were clusters of chrysotile, often with several hundreds of fibers. When estimates of these individual fibers were added to the total fiber count, the difference between the impacted and control houses became even greater. The increased concentrations in impacted houses were due primarily to short (less than 1 micrometer) fibers. Bulk samples did not reveal likely materials within the impacted houses to account for these differences. Thus high levels of waterborne asbestos were apparently the source of increased concentrations of airborne asbestos within these houses.
在一个社区的饮用水中检测到每升超过100亿根纤维的石棉污染。为评估水中石棉进入空气中的可能性,从接收受污染水的受影响房屋以及三间对照房屋采集了空气样本。在每间房屋内,在孔径为0.6微米的核孔滤膜上采集了三个样本,在孔径为0.8微米的密理博滤膜上也采集了三个样本。此外,还采集了可疑材料的大量样本和水样。受影响房屋中水中石棉的平均浓度为每升2400万根纤维(MFL),而对照房屋中仅为1.1 MFL。透射电子显微镜显示,受影响房屋中的空气中石棉浓度最高,空气中石棉浓度与水中浓度呈正相关。对于两种滤膜类型的纤维和质量测量,受影响房屋中的空气中石棉浓度显著更高:受影响房屋中核孔滤膜上的平均浓度为0.12根纤维/立方厘米和1.7纳克/立方米,密理博滤膜上为0.053根纤维/立方厘米和2.3纳克/立方米,而对照房屋中核孔滤膜上仅为0.037根纤维/立方厘米和0.31纳克/立方米,密理博滤膜上为0.0077根纤维/立方厘米和0.14纳克/立方米。在受影响房屋的空气样本中还检测到温石棉簇,通常含有数百根纤维。当将这些单根纤维的估计值加到总纤维计数中时,受影响房屋和对照房屋之间的差异变得更大。受影响房屋中浓度升高主要是由于短(小于1微米)纤维。大量样本未揭示受影响房屋内可能导致这些差异的物质。因此,高浓度的水中石棉显然是这些房屋中空气中石棉浓度升高的来源。