Natl Toxicol Program Tech Rep Ser. 1993 Sep;421:1-287.
Talc ore may contain several other minerals including calcite, dolomite, magnesite, tremolite, anthophyllite, antigorite, quartz, pyrophyllite, micas, or chlorites. Talc products are sold in a multitude of grades which have physical or functional characteristics especially suited for particular applications, so occupational and consumer exposures to talc are complex. Epidemiology studies have suggested an association between non-fibrous talc and lung cancer risk. Talc was nominated by the National Institute of Occupational Safety and Health (NIOSH) for study by the NTP because of widespread human exposure and because of the lack of adequate information on its chronic toxicity and potential carcinogenicity. Toxicology and carcinogenicity studies of talc (non-asbestiform, cosmetic grade), a finely powdered hydrous magnesium silicate, were conducted by exposing groups of F344/N rats to aerosols for 6 hours per day, 5 days per week for up to 113 weeks (males) or 122 weeks (females). Groups of B6C3F1 mice were exposed similarly for up to 104 weeks. LIFETIME STUDY IN RATS: Groups of 49 or 50 male and 50 female rats were exposed to aerosols of 0, 6, or 18 mg/m(3) talc until mortality in any exposure group reached 80% (113 weeks for males and 122 weeks for females). These exposures were selected based on 4-week inhalation studies of the terminal lung talc burden in F344/N rats; concentrations greater than 18 mg/m(3) were expected to overwhelm lung clearance mechanisms and impair lung function. These exposure concentrations provided a dose equivalent of 0, 2.8, or 8.4 mg/kg per day for male rats and 0, 3.2, or 9.6 mg/kg per day for female rats. In a special study, additional groups of 22 male and 22 female rats were similarly exposed and examined for interim pathology evaluations or pulmonary function tests after 6, 11, 18, and 24 months and lung biochemistry and cytology studies after 24 months. The talc aerosols had a median mass aerodynamic diameter of 2.7 mm in the 6 mg/m(3) chamber and a median diameter of 3.2 mm in the 18 mg/m(3) chamber, with geometric standard deviations of 1.9 mm. However, there was a 7-week period beginning at study week 11 during which the chamber concentration for the 18 mg/m(3) rats varied from approximately 30 to 40 mg/m(3) because of difficulties with the aerosol concentration monitoring system. Further, there was a 12-week period beginning at approximately week 70 during which there were difficulties in generating the talc aerosol, and the chamber concentrations for rats and mice were substantially lower than the target concentrations. Survival, Body Weights, and Clinical Findings: The survival of male and female rats exposed to talc was similar to that of the controls. Mean body weights of rats exposed to 18 mg/m(3) were slightly lower than those of controls after week 65. No clinical findings were attributed to talc exposure. Pathology Findings: Absolute and relative lung weights of male rats exposed to 18 mg/m(3) were significantly greater than those of controls at the 6-, 11-, and 18-month interim evaluations and at the end of the lifetime study, while those of female rats exposed to 18 mg/m(3) were significantly greater at the 11-, 18-, and 24-month interim evaluations and at the end of the lifetime study. Inhalation exposure of rats to talc produced a spectrum of inflammatory, reparative, and proliferative processes in the lungs. Granulomatous inflammation occurred in nearly all exposed rats and the severity increased with exposure duration and concentration. Hyperplasia of the alveolar epithelium and interstitial fibrosis occurred in or near foci of inflammation in many exposed rats, while squamous metaplasia of the alveolar epithelium and squamous cysts were also occasionally seen. Accumulations of macrophages (histiocytes), most containing talc particles, were found in the peribronchial lymphoid tissue of the lung and in the bronchial and mediastinal Iymph nodes. In female rats, the incidences of alveolar/bronchiolar adenoma, carcinoma, and adenoma or carcinoma (combined) in the 18 mg/m(8 mg/m(3) group were significantly greater than those of controls. The incidences of pulmonary neoplasms in exposed male rats were similar to those in controls. Minor alterations attributed to talc exposure were also observed in the upper respiratory tract. Hyperplasia of the respiratory epithelium of the nasal mucosa in males and accumulation of cytoplasmic, eosinophilic droplets in the nasal mucosal epithelium in male and female rats occurred with a concentration-related increased incidence in the exposed groups. Adrenal medulla pheochromocytomas [benign, malignant, or complex (combined)] occurred with a significant positive trend in male and female rats, and the incidences in the 18 mg/m(3) groups were significantly greater than those of controls. Although adrenal medulla hyperplasia occurred with similar frequency among exposed and control females, the incidences of hyperplasia in exposed males were significantly lower than in controls. Lung Talc Burden: Lung talc burdens of male and female rats exposed to 6 mg/m(3) were similar and increased progressively from 6 to 24 months. Lung talc burdens of females exposed to 18 mg/m(3) also increased progressively from 6 to 24 months, while those of males exposed to 18 mg/m(3) remained about the same after 18 months. Lung burdens were generally proportional to exposure concentration at each interim evaluation. Pulmonary Function, Bronchoalveolar Lavage, and Lung Biochemistry: In exposed male and female rats there was a concentration-related impairment of respiratory function which increased in severity with increasing exposure duration. The impairment was characterized by reductions in lung volume (total lung capacity, vital capacity, and forced vital capacity), lung compliance, gas exchange efficiency (carbon monoxide diffusing capacity), and nonuniform intrapulmonary gas distribution. After 24 months, males exposed to 6 mg/m(3) talc had a significant increase in beta-glucuronidase and polymorphonuclear leukocytes; males exposed 18 mg/m(3) had significant increases in b -glucuronidase, lactate dehydrogenase, alkaline phosphatase, and total protein in bronchoalveolar lavage fluid. All exposed females had significantly increased a-glucuronidase, lactate dehydrogenase, alkaline phosphatase, total protein, and polymorphonuclear leukocytes; 18 mg/m(3) females also had significantly increased glutathione reductase. Viability and phagocytic activity of macrophages recovered from lavage fluid were not affected by talc exposure. Total lung collagen was significantly increased in rats at both exposure concentrations after 24 months, while collagenous peptides in lavage fluid and the percentages of newly synthesized protein from females, but not males, were also significantly increased at the 6 or 18 mg/m(3) levels. In addition, lung proteinase activity, primarily cathepsin D-like activity, was significantly greater in exposed males and females. Rats exposed to talc also had significant increases in collagenous peptides and acid proteinase in lung homogenates. 2-YEAR STUDY IN MICE: Groups of 47 to 49 male and 48 to 50 female mice were exposed to aerosols containing 0, 6, or 18 mg/m(3) talc for up to 104 weeks. These exposures were selected based on 4-week inhalation studies of the terminal lung talc burden in B6C3F1 mice; concentrations greater than 18 mg/m(3) were expected to overwhelm lung clearance mechanisms and impair lung function. These exposure concentrations provide a dose equivalent of 0, 2, or 6 mg/kg per day for male mice and 0, 1.3, or 3.9 mg/kg per day for female mice. In a special study, additional groups of 39 or 40 male and 39 or 40 female mice similarly exposed were examined for interim pathology evaluations, lung biochemistry, and cytology studies after 6, 12, and 18 months of exposure. The talc aerosols had a median mass aerodynamic diameter of 3.3 mm with a geometric standard deviation of 1.9 mm in the 6 mg/m(3) chamber, and a median diameter of 3.6 mm with a geometric standard deviation of 2.0 mm in the 18 mg/m(3) chamber. Further, there was a 12-week period beginning at approximately week 70 during which there were difficulties in generating the talc aerosol, and the chamber concentrations for rats and mice were substantially lower than the target concentrations. Survival, Body Weights, and Clinical Findings: Survival and final mean body weights of male and female mice exposed to talc were similar to those of the controls. There were no clinical findings attributed to talc exposure. Pathology Findings: Inhalation exposure of mice to talc was associated with chronic active inflammation and the accumulation of macrophages in the lung. In contrast to rats, hyperplasia of the alveolar epithelium, squamous metaplasia, or interstitial fibrosis were not associated with the inflammatory response in mice, and the incidences of pulmonary neoplasms in exposed and control groups of mice were similar. Accumulations of macrophages (histiocytes) containing talc particles were also present in the bronchial Iymph node. In the upper respiratory tract, cytoplasmic alteration, consisting of the accumulation of cytoplasmic eosinophilic droplets in the nasal mucosal epithelium, occurred with a concentration-related increased incidence in exposed male and female mice. Lung Talc Burden: Lung talc burdens of mice exposed to 6 mg/m(3) were similar between males and females and increased progressively from 6 to 24 months, except for males at 18 months. The lung talc burdens of mice exposed to 18 mg/m(3) were also similar between the sexes at each interim evaluation. Although the talc burdens of males and females increased substantially from 6 to 24 months, the values at 12 and 18 months were similar. Generally, lung burdens of mice exposed to 18 mg/m(3) were disproportionately greater than those of mice exposed to 6 mg/m(3), suggesting that clearance of talc from the lung was impaired, or impaired to a greater extent, in mice exposed to 18 mg/m(3) than in mice exposed to 6 mg/m(3). Bronchoalveolar Lavage and Lung Biochemistry: Increases in total protein, beta-glucuronidase, lactate dehydrogenase, glutathione reductase, total nucleated cells, and polymorphonuclear leukocytes in bronchoalveolar lavage fluid were observed primarily in mice exposed to 18 mg/m(3), although some parameters were also increased in mice exposed to 6 mg/m(3). The amount of collagenous peptides in lavage fluid and total lung collagen were increased in male and female mice exposed to 18 mg/m(3). Acid proteinase activity, principally cathepsin D-like activity, of lung homogenate supernatant fluid was also significantly increased in mice at the 18 mg/m(3) exposure concentration. CONCLUSIONS: Under the conditions of these inhalation studies, there was some evidence of carcinogenic activity of talc in male F344/N rats based on an increased incidence of benign or malignant pheochromocytomas of the adrenal gland. There was clear evidence of carcinogenic activity of talc in female F344/N rats based on increased incidences of alveolar/bronchiolar adenomas and carcinomas of the lung and benign or malignant pheochromocytomas of the adrenal gland. There was no evidence of carcinogenic activity of talc in male or female B6C3F1 mice exposed to 6 or 18 mg/m(3). The principal toxic lesions associated with inhalation exposure to the same concentrations of talc in rats included chronic granulomatous inflammation, alveolar epithelial hyperplasia, squamous metaplasia and squamous cysts, and interstitial fibrosis of the lung. These lesions were accompanied by impaired pulmonary function characterized primarily by reduced lung volumes, reduced dynamic and/or quasistatic lung compliance, reduced gas exchange efficiency, and nonuniform intrapulmonary gas distribution. In mice, inhalation exposure to talc produced chronic inflammation of the lung with the accumulation of alveolar macrophages. Synonyms: talcum; agalite; emtal 596; non-asbestiform talc; non-fibrous talc; steatite; hydrous magnesium silicate
滑石矿可能含有几种其他矿物,包括方解石、白云石、菱镁矿、透闪石、直闪石、叶蛇纹石、石英、叶蜡石、云母或绿泥石。滑石产品以多种等级出售,这些等级具有特别适合特定应用的物理或功能特性,因此职业和消费者接触滑石的情况很复杂。流行病学研究表明,非纤维状滑石与肺癌风险之间存在关联。由于人类广泛接触滑石,且缺乏关于其慢性毒性和潜在致癌性的充分信息,美国国家职业安全与健康研究所(NIOSH)提名滑石由美国国家毒理学计划(NTP)进行研究。对滑石(非石棉状,化妆品级)进行了毒理学和致癌性研究,将多组F344/N大鼠每天暴露于气溶胶中6小时,每周5天,长达113周(雄性)或122周(雌性)。多组B6C3F1小鼠也进行了类似的暴露,长达104周。
将49或50只雄性和50只雌性大鼠分为几组,暴露于浓度为0、6或18 mg/m³的滑石气溶胶中,直到任何暴露组的死亡率达到80%(雄性为113周,雌性为122周)。这些暴露浓度是根据对F344/N大鼠终末肺滑石负荷的4周吸入研究选定的;预计浓度大于18 mg/m³会超过肺清除机制并损害肺功能。这些暴露浓度为雄性大鼠提供了相当于0、2.8或8.4 mg/kg/天的剂量,为雌性大鼠提供了相当于0、3.2或9.6 mg/kg/天的剂量。在一项特别研究中,另外几组22只雄性和22只雌性大鼠进行了类似的暴露,并在6、11、18和24个月后进行了中期病理学评估或肺功能测试,在24个月后进行了肺生物化学和细胞学研究。在6 mg/m³舱室中,滑石气溶胶的质量中值空气动力学直径为2.7 mm,在18 mg/m³舱室中为3.2 mm,几何标准差为1.9 mm。然而,从研究第11周开始的7周内,由于气溶胶浓度监测系统出现问题,18 mg/m³组大鼠的舱室浓度在约30至40 mg/m³之间变化。此外,从大约第70周开始的12周内,在产生滑石气溶胶方面出现困难,大鼠和小鼠的舱室浓度大大低于目标浓度。
生存、体重和临床发现:暴露于滑石的雄性和雌性大鼠的生存率与对照组相似。暴露于18 mg/m³的大鼠在第65周后的平均体重略低于对照组。没有临床发现可归因于滑石暴露。
在6、11和18个月的中期评估以及终身研究结束时,暴露于18 mg/m³的雄性大鼠的绝对和相对肺重量显著高于对照组,而暴露于18 mg/m³的雌性大鼠在11、18和24个月的中期评估以及终身研究结束时显著高于对照组。大鼠吸入滑石会在肺部产生一系列炎症、修复和增殖过程。几乎所有暴露的大鼠都发生了肉芽肿性炎症,其严重程度随暴露时间和浓度增加。许多暴露的大鼠在炎症灶内或附近出现肺泡上皮增生和间质纤维化,同时也偶尔可见肺泡上皮鳞状化生和鳞状囊肿。在肺支气管周围淋巴组织以及支气管和纵隔淋巴结中发现了巨噬细胞(组织细胞)的聚集,其中大多数含有滑石颗粒。在雌性大鼠中,暴露于18 mg/m³的肺泡/细支气管腺瘤、癌以及腺瘤或癌(合并)的发生率显著高于对照组。暴露的雄性大鼠肺部肿瘤的发生率与对照组相似。在呼吸道上部也观察到了归因于滑石暴露的轻微变化。雄性大鼠鼻黏膜呼吸上皮增生,雄性和雌性大鼠鼻黏膜上皮中出现嗜酸性细胞质液滴聚集,且在暴露组中发生率与浓度相关增加。雄性和雌性大鼠肾上腺髓质嗜铬细胞瘤(良性、恶性或复合型(合并))的发生率呈显著正趋势,18 mg/m³组的发生率显著高于对照组。尽管暴露和对照雌性中肾上腺髓质增生的频率相似,但暴露雄性中的增生发生率显著低于对照组。
暴露于6 mg/m³的雄性和雌性大鼠的肺滑石负荷相似,从6个月到24个月逐渐增加。暴露于18 mg/m³的雌性大鼠的肺滑石负荷也从6个月到24个月逐渐增加,而暴露于18 mg/m³的雄性大鼠在18个月后保持大致相同。在每次中期评估时,肺负荷通常与暴露浓度成正比。
肺功能、支气管肺泡灌洗和肺生物化学:在暴露的雄性和雌性大鼠中,存在与浓度相关的呼吸功能损害,其严重程度随暴露时间增加而加重。这种损害的特征是肺容积(肺总量、肺活量和用力肺活量)、肺顺应性、气体交换效率(一氧化碳弥散量)降低以及肺内气体分布不均匀。24个月后,暴露于6 mg/m³滑石的雄性大鼠β - 葡萄糖醛酸酶和多形核白细胞显著增加;暴露于18 mg/m³的雄性大鼠支气管肺泡灌洗液中的β - 葡萄糖醛酸酶(b - glucuronidase)、乳酸脱氢酶、碱性磷酸酶和总蛋白显著增加。所有暴露的雌性大鼠α - 葡萄糖醛酸酶、乳酸脱氢酶、碱性磷酸酶、总蛋白和多形核白细胞显著增加;18 mg/m³组的雌性大鼠谷胱甘肽还原酶也显著增加。从灌洗液中回收的巨噬细胞的活力和吞噬活性不受滑石暴露的影响。24个月后,两种暴露浓度的大鼠肺总胶原蛋白均显著增加,而在6或18 mg/m³水平下,灌洗液中的胶原肽以及雌性(而非雄性)新合成蛋白的百分比也显著增加。此外,暴露的雄性和雌性大鼠肺蛋白酶活性(主要是组织蛋白酶D样活性)显著更高。暴露于滑石的大鼠肺匀浆中的胶原肽和酸性蛋白酶也显著增加。
将47至49只雄性和48至50只雌性小鼠分为几组,暴露于含有0、6或18 mg/m³滑石的气溶胶中,长达104周。这些暴露浓度是根据对B6C3F1小鼠终末肺滑石负荷的4周吸入研究选定的;预计浓度大于18 mg/m³会超过肺清除机制并损害肺功能。这些暴露浓度为雄性小鼠提供了相当于0、2或6 mg/kg/天的剂量,为雌性小鼠提供了相当于0、1.3或3.9 mg/kg/天的剂量。在一项特别研究中,另外几组39或40只雄性和39或40只雌性小鼠进行了类似的暴露,并在暴露6、12和18个月后进行了中期病理学评估、肺生物化学和细胞学研究。在6 mg/m³舱室中,滑石气溶胶的质量中值空气动力学直径为3.3 mm,几何标准差为1.9 mm,在18 mg/m³舱室中中值直径为3.6 mm,几何标准差为2.0 mm。此外,从大约第70周开始的12周内,在产生滑石气溶胶方面出现困难,大鼠和小鼠的舱室浓度大大低于目标浓度。
生存、体重和临床发现:暴露于滑石的雄性和雌性小鼠的生存率和最终平均体重与对照组相似。没有临床发现可归因于滑石暴露。
小鼠吸入滑石与肺部慢性活动性炎症和巨噬细胞聚集有关。与大鼠不同,肺泡上皮增生、鳞状化生或间质纤维化与小鼠的炎症反应无关,暴露组和对照组小鼠肺部肿瘤的发生率相似。在支气管淋巴结中也存在含有滑石颗粒 的巨噬细胞(组织细胞)聚集。在呼吸道上部,暴露的雄性和雌性小鼠鼻黏膜上皮中出现细胞质嗜酸性液滴聚集的细胞质改变,且发生率与浓度相关增加。
暴露于6 mg/m³的小鼠雄性和雌性的肺滑石负荷相似,从6个月到24个月逐渐增加,但18个月时的雄性小鼠除外。暴露于18 mg/m³的小鼠在每次中期评估时两性的肺滑石负荷也相似。尽管雄性和雌性的滑石负荷从6个月到24个月大幅增加,但12个月和18个月时的值相似。一般来说,暴露于18 mg/m³的小鼠的肺负荷比暴露于6 mg/m³的小鼠不成比例地更大,这表明暴露于18 mg/m³的小鼠中滑石从肺部的清除受到损害,或受到的损害程度更大。
支气管肺泡灌洗液中总蛋白、β - 葡萄糖醛酸酶、乳酸脱氢酶、谷胱甘肽还原酶、总核细胞和多形核白细胞的增加主要在暴露于18 mg/m³的小鼠中观察到,尽管在暴露于6 mg/m³的小鼠中一些参数也有所增加。暴露于18 mg/m³的雄性和雌性小鼠灌洗液中的胶原肽量和肺总胶原蛋白增加。在18 mg/m³暴露浓度下,小鼠肺匀浆上清液的酸性蛋白酶活性(主要是组织蛋白酶D样活性)也显著增加。
在这些吸入研究的条件下,基于肾上腺良性或恶性嗜铬细胞瘤发生率增加,有一些证据表明滑石对雄性F344/N大鼠具有致癌活性。基于肺部肺泡/细支气管腺瘤和癌以及肾上腺良性或恶性嗜铬细胞瘤发生率增加,有明确证据表明滑石对雌性F344/N大鼠具有致癌活性。没有证据表明暴露于6或18 mg/m³的雄性或雌性B6C3F1小鼠中滑石具有致癌活性。与吸入相同浓度滑石相关的大鼠主要毒性病变包括慢性肉芽肿性炎症、肺泡上皮增生、鳞状化生和鳞状囊肿以及肺间质纤维化。这些病变伴有肺功能损害,主要表现为肺容积减小、动态和/或准静态肺顺应性降低、气体交换效率降低以及肺内气体分布不均匀。在小鼠中,吸入滑石会导致肺部慢性炎症和肺泡巨噬细胞聚集。
滑石粉;块滑石;emtal 596;非石棉状滑石;非纤维状滑石;块滑石;水合硅酸镁