Saitoh K, Takizawa Y, Muto H, Hirano K
Department of Public Health, Akita University School of Medicine.
Nihon Eiseigaku Zasshi. 1992 Oct;47(4):851-60. doi: 10.1265/jjh.47.851.
The identification and concentration of asbestos fibers in tap drinking water supplied in a central area of Akita Prefecture, Japan, were determined by phase-contrast microscopy and a scanning electron microscope equipped with an energy-dispersive X-ray microanalyzer. The following results were obtained. 1. Asbestos fibers were found in the tap water from two areas in which an asbestos-cement pipe was used for public water supply. The concentrations of asbestos fibers in the tap water were 2.7 x 10(4) to 27.0 x 10(4) fibers per liter of water in area A and 10.0 x 10(4) to 21.0 x 10(4) in area B. On the other hand, no asbestos fiber contamination was observed in tap water of area C, which shared a common water source with area A. A vinyl chloride pipe was used over the entire length of the water supply in route C. 2. Crocidolite was the predominant type of asbestos fiber detected in the tap water. Chrysotile and a mixture of chrysotile and amosite were also observed. 3. Almost all asbestos fibers detected in the tap water possessed the form of thick or sheaved fibers with lengths ranging from ca. 5 to 10 microns. Their shapes were very different from those of asbestos fibers found in the atmosphere. The typical form of the latter is short (ca. 1 micron in length) and needle-like. 4. It was suggested that the contamination of asbestos fibers in the tap water was caused by erosion and peeling off of the inner wall of the asbestos-cement pipe used as a conduit. In order to evaluate the safety of drinking water in Japan, an extensive survey on asbestos-fiber contamination in tap water is necessary.
采用相差显微镜和配备能量色散X射线微分析仪的扫描电子显微镜,对日本秋田县中部地区供应的自来水进行了石棉纤维的鉴定和浓度测定。结果如下:1. 在两个使用石棉水泥管进行公共供水的地区的自来水中发现了石棉纤维。地区A自来水中石棉纤维的浓度为每升水2.7×10⁴至27.0×10⁴根纤维,地区B为10.0×10⁴至21.0×10⁴根。另一方面,与地区A共用同一水源的地区C的自来水中未观察到石棉纤维污染。地区C的供水全程使用的是氯乙烯管。2. 青石棉是在自来水中检测到的主要石棉纤维类型。也观察到了温石棉以及温石棉和铁石棉的混合物。3. 在自来水中检测到的几乎所有石棉纤维都呈粗纤维或束状纤维形式,长度约为5至10微米。它们的形状与大气中发现的石棉纤维非常不同。后者的典型形式是短的(长度约1微米)且呈针状。4. 有人认为自来水中石棉纤维的污染是由用作输水管道的石棉水泥管内壁的侵蚀和剥落造成的。为了评估日本饮用水的安全性,有必要对自来水中石棉纤维污染进行广泛调查。