Natl Toxicol Program Tech Rep Ser. 2011 Aug(564):1-190.
In the early to mid 1990s, 1-bromopropane was used primarily as an intermediate in the production of pesticides, quaternary ammonium compounds, flavors and fragrances, pharmaceuticals, and other chemicals in well-controlled, closed processes. In the mid to late 1990s, it was introduced as a less toxic replacement for methylene chloride in emissive applications such as vapor and immersion degreasing operations and critical cleaning of electronics and metals. 1-Bromopropane was also introduced as a nonflammable, nontoxic, fast-drying, and inexpensive solvent for adhesive resins, and has been marketed as a replacement for ozone depleting refrigerants. 1-Bromopropane was nominated for study by the Occupational Safety and Health Administration based on the potential for widespread occupational and environmental exposure and a lack of toxicity and carcinogenicity data. Male and female F344/N rats and B6C3F1 mice were exposed to 1-bromopropane (99% or greater pure) by inhalation for 2 weeks, 3 months, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and Escherichia coli and mouse peripheral blood. 2-WEEK STUDY IN RATS: Groups of five male and five female rats were exposed to 1-bromopropane vapor at concentrations of 0, 125, 250, 500, 1,000, or 2,000 ppm, 6 hours plus T90 (12 minutes) per day, 5 days per week for 16 days. All rats survived to the end of the study except one 500 ppm male. Mean body weights of 2,000 ppm rats were significantly less than those of the chamber controls. The absolute kidney weight of 1,000 ppm males, relative kidney weights of all exposed groups of males, and absolute and relative kidney weights of all exposed groups of females were significantly increased. The absolute and relative liver weights of 1,000 ppm males, relative liver weights of 500 and 2,000 ppm males, and absolute and relative liver weights of 500 ppm or greater females were significantly increased. Nasal lesions included suppurative inflammation in males exposed to 500 ppm or greater, respiratory epithelial necrosis in 1,000 and 2,000 ppm males, and respiratory epithelial regeneration in 1,000 and 2,000 ppm females. 2-WEEK STUDY IN MICE: Groups of five male and five female mice were exposed to 1-bromopropane vapor at concentrations of 0, 125, 250, 500, 1,000, or 2,000 ppm, 6 hours plus T90 (12 minutes) per day, 5 days per week for 17 days. All 2,000 ppm males, two 2,000 ppm females, four 500 ppm males, one 1,000 ppm male, and one 1,000 ppm female died early. The mean body weight gain of 1,000 ppm males was significantly less than that of the chamber controls. Abnormal breathing, lethargy, and eye discharge were observed primarily during week 1 in groups exposed to 500 ppm or greater. Liver weights of 1,000 ppm males and of females exposed to 500 ppm or greater were significantly increased. Kidney weights of 1,000 and 2,000 ppm females were significantly increased. Microscopic lesions related to 1-bromopropane exposure occurred in the lung, liver, and nose of males and females and were primarily seen in mice exposed to 500 ppm or greater. 3-MONTH STUDY IN RATS: Groups of 10 male and 10 female rats were exposed to 1-bromopropane vapor at concentrations of 0, 62.5, 125, 250, 500, or 1,000 ppm, 6 hours plus T90 (10 minutes) per day, 5 days per week for 14 weeks. Additional clinical pathology groups of 10 male and 10 female rats were exposed to the same concentrations for 23 days. All rats survived to the end of the study. Mean body weights of 1,000 ppm males were significantly less than those of the chamber controls. The increases in sorbitol dehydrogenase activities in 500 ppm males and 1,000 ppm males and females were consistent with the histopathologic evidence of mild hepatotoxicity caused by 1-bromopropane. Liver weights of males exposed to 250 ppm or greater and of females exposed to 125 ppm or greater were significantly increased. Spleen and kidney weights of 1,000 ppm females were significantly increased. Exposure concentration-related decreases of 28% in sperm motility and 37% in sperm counts were seen in the 1,000 ppm group of male rats. Female rats in all three exposure groups evaluated exhibited altered estrous cycles, spending significantly more time in extended estrus and less time in extended diestrus. The incidences of cytoplasmic vacuolization of the liver were significantly increased in males exposed to 250 ppm or greater and in females exposed to 500 ppm or greater. Hepatocyte degeneration was also observed in 1,000 ppm females. 3-MONTH STUDY IN MICE: Groups of 10 male and 10 female mice were exposed to 1-bromopropane vapor at concentrations of 0, 62.5, 125, 250, or 500 ppm, 6 hours plus T90 (10 minutes) per day, 5 days per week for 14 weeks. One 250 ppm male and four males and five females in the 500 ppm groups died early. Mean body weights of exposed groups were similar to those of the chamber controls. Lethargy was observed in males and females exposed to 500 ppm, and abnormal breathing was observed in moribund mice. The kidney, liver, and lung weights of 500 ppm females were significantly greater than those of the chamber controls. The kidney weights of 500 ppm males were significantly decreased. Sperm counts in the 500 ppm group of male mice were 28% less than that in the chamber controls. Female mice exhibited altered estrous cycles, with females in the 500 ppm group spending significantly more time in extended diestrus and those in the 250 ppm group spending significantly more time in extended estrus compared to the chamber controls. Nonneoplastic lesions were observed in the nose, larynx, trachea, lung, and liver of 500 ppm males and females and in the adrenal cortex of 500 ppm females. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female rats were exposed to 1-bromopropane vapor at concentrations of 0, 125, 250, or 500 ppm, 6 hours plus T90 (10 minutes) per day, 5 days per week for 105 weeks. Survival of 500 ppm males was significantly less than that of the chamber control group. Mean body weights of exposed groups were similar to those of the chamber controls. Increased incidences of macroscopic, soft, pale-yellow to green, variably sized nodules were seen predominantly in the nose and skin of exposed rats. The number of animals with multiple masses was increased in the 500 ppm groups. In most cases, these lesions were microscopically shown to be suppurative inflammation, many with Splendore-Hoeppli material. The incidence of adenoma of the large intestine (colon or rectum) was significantly greater in 500 ppm females than in the chamber control group. The incidence of adenoma of the large intestine in 250 ppm males exceeded the historical control ranges for inhalation studies and all routes. The incidences of keratoacanthoma, basal cell adenoma, basal cell carcinoma, or squamous cell carcinoma (combined) were significantly greater in all exposed groups of males than in the chamber control group and exceeded the historical control range for inhalation studies. The incidences of keratoacanthoma and of keratoacanthoma or squamous cell carcinoma (combined) in 250 and 500 ppm males were also significantly increased and exceeded the historical control ranges for inhalation studies. In 500 ppm females, the incidence of squamous cell papilloma, keratoacanthoma, basal cell adenoma, or basal cell carcinoma (combined) exceeded the historical control range for inhalation studies. The incidence of malignant mesothelioma was significantly greater in 500 ppm males than in the chamber control group. The incidences of pancreatic islet adenoma in all exposed groups of males and of pancreatic islet adenoma or carcinoma (combined) in 125 and 250 ppm males were significantly increased. Treatment-related nonneoplastic lesions were observed in the respiratory system of exposed male and female rats. In the nose, the incidences of suppurative chronic inflammation, chronic active inflammation, glandular hyperplasia, respiratory epithelial hyperplasia (females), and respiratory metaplasia of the olfactory epithelium (females) were increased in all exposed groups. In the larynx, the incidences of chronic active inflammation and squamous metaplasia (except 125 ppm females) were increased in all exposed groups, and the incidences of suppurative chronic inflammation were increased in the 500 ppm groups. Also, chronic inflammation of the lung was observed in the 500 ppm females. In the trachea, there were increased incidences of chronic active inflammation in all exposed groups of females and 500 ppm males, and the incidence of epithelial hyperplasia was increased in 500 ppm females. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female mice were exposed to 1-bromopropane vapor at concentrations of 0, 62.5, 125, or 250 ppm, 6 hours plus T90 (10 minutes) per day, 5 days per week for 105 weeks. Survival of exposed groups was similar to that of the chamber controls. Mean body weights of all exposed groups were similar to those of the chamber controls throughout the study. In the females, there were increased incidences of alveolar/bronchiolar adenoma, alveolar/bronchiolar carcinoma, and alveolar/bronchiolar adenoma or carcinoma (combined); the incidences of alveolar/bronchiolar adenoma or carcinoma (combined) were significantly increased in all exposed groups of females. There were significantly increased incidences of cytoplasmic vacuolization of the bronchiolar epithelium in all exposed male groups and regeneration of the bronchiolar epithelium in all exposed groups of males and females. In the nose, there were significantly increased incidences of cytoplasmic vacuolization of the respiratory epithelium in all exposed groups of males and in 125 and 250 ppm females. There were significantly increased incidences of respiratory epithelial hyperplasia in all exposed female groups and in 62.5 and 250 ppm males. (ABSTRACT TRUNCATED)
在20世纪90年代初至中期,1-溴丙烷主要用作农药、季铵化合物、香料、药品及其他化学品生产过程中的中间体,这些生产过程受到严格控制且在封闭环境中进行。在20世纪90年代中期至后期,它被引入作为二氯甲烷在诸如蒸汽脱脂、浸泡脱脂操作以及电子和金属部件的精密清洗等排放应用中的低毒替代品。1-溴丙烷还被用作粘性树脂的不燃、无毒、快干且廉价的溶剂,并作为消耗臭氧层制冷剂的替代品进行销售。基于其广泛的职业和环境暴露可能性以及缺乏毒性和致癌性数据,职业安全与健康管理局将1-溴丙烷列为研究对象。将雄性和雌性F344/N大鼠以及B6C3F1小鼠通过吸入方式暴露于纯度为99%或更高的1-溴丙烷中,暴露时间分别为2周、3个月或2年。在鼠伤寒沙门氏菌、大肠杆菌以及小鼠外周血中进行了遗传毒理学研究。
大鼠2周研究:将每组5只雄性和5只雌性大鼠暴露于浓度为0、125、250、500、1000或2000 ppm的1-溴丙烷蒸汽中,每天暴露6小时加T90(12分钟),每周暴露5天,共暴露16天。除一只500 ppm的雄性大鼠外,所有大鼠均存活至研究结束。2000 ppm组大鼠的平均体重显著低于饲养室对照组。1000 ppm雄性大鼠的绝对肾脏重量、所有暴露组雄性大鼠的相对肾脏重量以及所有暴露组雌性大鼠的绝对和相对肾脏重量均显著增加。1000 ppm雄性大鼠的绝对和相对肝脏重量、500和2000 ppm雄性大鼠的相对肝脏重量以及500 ppm及以上雌性大鼠的绝对和相对肝脏重量均显著增加。鼻部病变包括暴露于500 ppm及以上浓度的雄性大鼠出现化脓性炎症,1000和2000 ppm雄性大鼠出现呼吸上皮坏死,1000和2000 ppm雌性大鼠出现呼吸上皮再生。
小鼠2周研究:将每组5只雄性和5只雌性小鼠暴露于浓度为0、125、250、500、1000或2000 ppm的1-溴丙烷蒸汽中,每天暴露6小时加T90(12分钟),每周暴露5天,共暴露17天。所有2000 ppm的雄性小鼠、2只2000 ppm的雌性小鼠、4只500 ppm的雄性小鼠、1只1000 ppm的雄性小鼠和1只1000 ppm的雌性小鼠均提前死亡。1000 ppm雄性小鼠的平均体重增加显著低于饲养室对照组。主要在暴露于500 ppm及以上浓度的组中,在第1周观察到异常呼吸、嗜睡和眼部分泌物增多。1000 ppm雄性小鼠以及暴露于500 ppm及以上浓度的雌性小鼠的肝脏重量显著增加。1000和2000 ppm雌性小鼠的肾脏重量显著增加。与1-溴丙烷暴露相关的微观病变出现在雄性和雌性小鼠的肺、肝脏和鼻子中,主要见于暴露于500 ppm及以上浓度的小鼠。
大鼠3个月研究:将每组10只雄性和10只雌性大鼠暴露于浓度为0、62.5、125、250、500或1000 ppm的1-溴丙烷蒸汽中,每天暴露6小时加T90(10分钟),每周暴露5天,共暴露14周。另外将每组10只雄性和10只雌性大鼠暴露于相同浓度下23天作为临床病理学研究组。所有大鼠均存活至研究结束。1000 ppm雄性大鼠的平均体重显著低于饲养室对照组。500 ppm雄性大鼠以及1000 ppm雄性和雌性大鼠的山梨醇脱氢酶活性增加,这与1-溴丙烷引起的轻度肝毒性组织病理学证据一致。暴露于250 ppm及以上浓度的雄性大鼠以及暴露于125 ppm及以上浓度的雌性大鼠的肝脏重量显著增加。1000 ppm雌性大鼠的脾脏和肾脏重量显著增加。在1000 ppm雄性大鼠组中,精子活力下降28%,精子数量下降37%。在所有三个暴露组的雌性大鼠中,发情周期均发生改变,处于延长发情期的时间显著增加,处于延长间情期的时间显著减少。暴露于250 ppm及以上浓度的雄性大鼠以及暴露于500 ppm及以上浓度的雌性大鼠肝脏细胞质空泡化的发生率显著增加。在1000 ppm雌性大鼠中也观察到肝细胞变性。
小鼠3个月研究:将每组10只雄性和10只雌性小鼠暴露于浓度为0、62.5、125、250或500 ppm的1-溴丙烷蒸汽中,每天暴露6小时加T90(10分钟),每周暴露5天,共暴露14周。一只250 ppm的雄性小鼠以及500 ppm组中的4只雄性小鼠和5只雌性小鼠提前死亡。暴露组的平均体重与饲养室对照组相似。在暴露于500 ppm的雄性和雌性小鼠中观察到嗜睡,在濒死小鼠中观察到异常呼吸。500 ppm雌性小鼠的肾脏、肝脏和肺重量显著大于饲养室对照组。500 ppm雄性小鼠的肾脏重量显著降低。500 ppm雄性小鼠组的精子数量比饲养室对照组少28%。雌性小鼠发情周期发生改变,与饲养室对照组相比,500 ppm组雌性小鼠处于延长间情期的时间显著增加,250 ppm组雌性小鼠处于延长发情期的时间显著增加。在500 ppm雄性和雌性小鼠的鼻子、喉、气管、肺和肝脏以及500 ppm雌性小鼠的肾上腺皮质中观察到非肿瘤性病变。
大鼠2年研究:将每组50只雄性和50只雌性大鼠暴露于浓度为0、125、250或500 ppm的1-溴丙烷蒸汽中,每天暴露6小时加T90(10分钟),每周暴露5天,共暴露105周。500 ppm雄性大鼠的存活率显著低于饲养室对照组。暴露组的平均体重与饲养室对照组相似。在暴露大鼠的鼻子和皮肤中,肉眼可见的、柔软的、浅黄色至绿色、大小不一的结节发生率增加,主要在500 ppm组中出现多个肿块的动物数量增加。在大多数情况下,这些病变在显微镜下显示为化脓性炎症,许多伴有Splendore-Hoeppli物质。500 ppm雌性大鼠的大肠(结肠或直肠)腺瘤发生率显著高于饲养室对照组。250 ppm雄性大鼠的大肠腺瘤发生率超过了吸入研究及所有途径的历史对照范围。所有暴露组雄性大鼠的角化棘皮瘤、基底细胞腺瘤、基底细胞癌或鳞状细胞癌(合并)发生率显著高于饲养室对照组,且超过了吸入研究的历史对照范围。250和500 ppm雄性大鼠的角化棘皮瘤以及角化棘皮瘤或鳞状细胞癌(合并)发生率也显著增加,超过了吸入研究的历史对照范围。在500 ppm雌性大鼠中,鳞状细胞乳头瘤、角化棘皮瘤、基底细胞腺瘤或基底细胞癌(合并)发生率超过了吸入研究的历史对照范围。500 ppm雄性大鼠的恶性间皮瘤发生率显著高于饲养室对照组。所有暴露组雄性大鼠的胰岛腺瘤发生率以及125和250 ppm雄性大鼠的胰岛腺瘤或癌(合并)发生率显著增加。在暴露的雄性和雌性大鼠的呼吸系统中观察到与治疗相关的非肿瘤性病变。在鼻子中,所有暴露组的化脓性慢性炎症、慢性活动性炎症、腺体增生、呼吸上皮增生(雌性)以及嗅上皮呼吸化生(雌性)发生率均增加。在喉中,所有暴露组的慢性活动性炎症和鳞状化生(125 ppm雌性除外)发生率增加,500 ppm组的化脓性慢性炎症发生率增加。此外,在500 ppm雌性大鼠中观察到肺部慢性炎症。在气管中,所有暴露组雌性大鼠以及500 ppm雄性大鼠的慢性活动性炎症发生率增加,500 ppm雌性大鼠的上皮增生发生率增加。
小鼠2年研究:将每组50只雄性和50只雌性小鼠暴露于浓度为0、62.5、125或250 ppm的1-溴丙烷蒸汽中,每天暴露6小时加T90(10分钟),每周暴露5天,共暴露105周。暴露组的存活率与饲养室对照组相似。在整个研究过程中,所有暴露组的平均体重与饲养室对照组相似。在雌性小鼠中,肺泡/细支气管腺瘤、肺泡/细支气管癌以及肺泡/细支气管腺瘤或癌(合并)的发生率增加;所有暴露组雌性小鼠的肺泡/细支气管腺瘤或癌(合并)发生率均显著增加。所有暴露组雄性小鼠的细支气管上皮细胞质空泡化发生率显著增加,所有暴露组雄性和雌性小鼠的细支气管上皮再生发生率显著增加。在鼻子中,所有暴露组雄性小鼠以及125和250 ppm雌性小鼠的呼吸上皮细胞质空泡化发生率显著增加。所有暴露组雌性小鼠以及62.5和250 ppm雄性小鼠的呼吸上皮增生发生率显著增加。(摘要截断)