Kamstrup O, Ellehauge A, Bellmann B, Chevalier J, Davis J M G
Rockwool International A/S, Hovedgaden 584, DK-2640 Hedehusene, Denmark.
Ann Occup Hyg. 2004 Mar;48(2):91-104. doi: 10.1093/annhyg/meg093.
Pathology results after subchronic inhalation in rats of three separate fibres representing the new biosoluble high-aluminium low-silica HT type stone wool are given, and the results were compared with the results from a similar study done with the traditional stone wool MMVF21. Male Wistar rats were exposed at one exposure level by nose-only inhalation to well-characterized fibre test atmospheres. The fibres had been size selected to be largely rat respirable. The target dose was an exposure to 150 long fibres/ml (length>20 microm) in each group, and this dose was achieved for all the fibres. The negative control groups were exposed to filtered air. The exposure duration was 6 h/day, 5 days/week for 3 months, with a subsequent non-exposure period lasting 3 months. The rats were killed 1 week after the last exposure and additional post-exposure kills were performed at 1.5 and 3 months to monitor the progression of pulmonary change and fibre numbers in the lung. The assessments included bronchoalveolar lavage fluid (BALF) for evaluation of inflammatory response (e.g. protein content, enzymes, increase in polymorphonuclear leucocytes) and measurement of cell proliferation, assessment of early fibrosis through histological examination and comparison of body weight and lung lobe weights. After exposure of rats to the new biosoluble fibres no biologically significant effects were observed except that a statistically significant increase in lung weight was observed up to 1.5 months post-exposure in all three treatment groups. At 3 months post-exposure, the small increase was no longer significant. The increase in lung weight was still present in the MMVF21 group at the 3 months post-exposure kill. After 3 months exposure, lung retention of long fibres (length>20 microm) varied from 0.4 to 5.2 x 10(6) per lung for the biosoluble fibres. At 3 months post-exposure, the long fibre concentration in the lungs had decreased to 1-7% of this figure. The fibre with the relatively highest biopersistence (RIF41001) showed the highest fibre retention. The retention of the more biopersistent traditional stone wool MMVF21 was 5.7 x 10(6) per rat lung after 3 months exposure and had decreased to 64% of this figure at 3 months post-exposure. There was no clear difference in the bronchoalveolar lavage fluid cell concentration and percentage of cells between MMVF21 and the HT groups. Fibre inhalation caused a significant increase after 3 months in all the biochemical parameters measured in the BALF. Cell proliferation was enhanced at the end of exposure for MMVF21 for all three labelling indices, but only for the bronchiolar epithelium in the RIF41001 group and for alveolar parenchymal cells in the RIF43006-1 group. At the termination of the 3 month exposure period, as well as after 1.5 and 3 month recovery periods, minimal morphological changes were diagnosed in the biosoluble fibre groups. These changes included alveolar macrophage aggregation and/or microgranulomas at the bronchiolar-alveolar junction in the few rats affected. No fibrogenic potential was noted for any of the three fibres. No clear-cut difference between the different biosoluble fibre types was noted. In the MMVF21 group, minimal interstitial fibrosis was observed that gradually decreased after the 1.5 and 3 month non-exposure periods. In this study, the pathological changes found in the lungs of exposed rats were in accordance with the pathology previously reported from full lifespan inhalation studies. This may indicate that for fibres belonging to the man-made vitreous fibres group a well conducted biopersistence study is sufficient to predict possible pathogenic effects for new fibre types. The biological parameters examined in a 90 day study may indicate little additional information to contribute to the prediction of the outcome of carcinogenicity studies.
给出了大鼠经亚慢性吸入三种分别代表新型生物可溶高铝低硅HT型石棉的纤维后的病理学结果,并将结果与用传统石棉MMVF21进行的类似研究结果进行了比较。雄性Wistar大鼠通过仅经鼻吸入暴露于特征明确的纤维测试气氛中,暴露水平为一种。纤维经过尺寸筛选,主要为大鼠可吸入的。每组的目标剂量是暴露于150根长纤维/毫升(长度>20微米),所有纤维均达到了该剂量。阴性对照组暴露于过滤空气中。暴露持续时间为每天6小时,每周5天,持续3个月,随后有3个月的非暴露期。在最后一次暴露后1周处死大鼠,并在暴露后1.5个月和3个月进行额外的处死,以监测肺部变化的进展和肺内纤维数量。评估包括支气管肺泡灌洗液(BALF)以评估炎症反应(如蛋白质含量、酶、多形核白细胞增加)和细胞增殖的测量,通过组织学检查评估早期纤维化以及比较体重和肺叶重量。大鼠暴露于新型生物可溶纤维后,未观察到生物学上显著的影响,只是在所有三个治疗组中,暴露后1.5个月内观察到肺重量有统计学上的显著增加。在暴露后3个月,这种小幅增加不再显著。在暴露后3个月处死时,MMVF21组仍存在肺重量增加。暴露3个月后,生物可溶纤维的长纤维(长度>20微米)肺内滞留量为每肺0.4至5.2×10⁶根。在暴露后3个月,肺内长纤维浓度已降至该数值的1 - 7%。生物持久性相对最高的纤维(RIF41001)显示出最高的纤维滞留。暴露3个月后,传统石棉MMVF₂₁每只大鼠肺内的滞留量为5.7×10⁶根,在暴露后3个月降至该数值的64%。MMVF₂₁组和HT组之间支气管肺泡灌洗液细胞浓度和细胞百分比没有明显差异。纤维吸入3个月后,BALF中所有测量的生化参数均显著增加。对于MMVF₂₁,在暴露结束时,所有三个标记指数的细胞增殖均增强,但仅RIF41001组的细支气管上皮细胞和RIF43006 - 1组的肺泡实质细胞出现这种情况。在3个月暴露期结束时以及1.5个月和3个月恢复期后,生物可溶纤维组诊断出的形态学变化最小。这些变化包括少数受影响大鼠的细支气管 - 肺泡交界处的肺泡巨噬细胞聚集和/或微肉芽肿。三种纤维均未发现有纤维化潜能。不同生物可溶纤维类型之间未发现明显差异。在MMVF₂₁组中,观察到最小程度的间质纤维化,在1.5个月和3个月的非暴露期后逐渐减少。在本研究中,暴露大鼠肺部发现的病理变化与先前全寿命吸入研究报告的病理情况一致。这可能表明,对于属于人造玻璃纤维组的纤维,进行良好的生物持久性研究足以预测新纤维类型可能的致病作用。在90天研究中检查的生物学参数可能表明对致癌性研究结果的预测几乎没有额外的贡献。