Natl Toxicol Program Tech Rep Ser. 1999 Feb;472:1-242.
Isobutyraldehyde, a branched alkyl aldehyde, is used as a chemical intermediate and flavoring agent. It was nominated by the National Cancer Institute for toxicity and carcinogenicity studies by the NTP. Reasons for nomination and selection of isobutyraldehyde for study included its high potential for human exposure as suggested by its high production volume, its use as a chemical intermediate and food flavoring agent, suspicion of carcinogenicity due to an increased incidence of cancer at an aldehyde manufacturing plant where workers were exposed to a variety of aldehydes, its structural relationship to formaldehyde (a nasal carcinogen in rats), and the lack of toxicity and carcinogenicity studies on isobutyraldehyde in animals. Although human exposure occurs orally, dermally, or via inhalation, the inhalation route of exposure was selected for these animal studies because of the instability of isobutyraldehyde in water and feed. Male and female F344/N rats and B6C3F1 mice were exposed to isobutyraldehyde (approximately 99% pure) by inhalation for 13 weeks or 2 years. Genetic toxicology studies were conducted in vitro in Salmonella typhimurium, L5178Y mouse lymphoma cells, and cultured Chinese hamster ovary cells; in vivo tests were conducted in Drosophila melanogaster germ cells and bone marrow cells of rats and mice. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were exposed to 0, 500, 1,000, 2,000, 4,000, or 8,000 ppm isobutyraldehyde by inhalation, 6 hours per day, 5 days a week, for 13 weeks. All rats exposed to 8,000 ppm died before the end of the study. Three male rats and six female rats in the 4,000 ppm groups and one female in the 500 ppm group died before the end of the study. The final mean body weight of male rats in the 4,000 ppm group and the body weight gains of 4,000 ppm males and females were significantly less than those of the chamber controls. Clinical findings in rats exposed to 4,000 or 8,000 ppm included abnormal respiratory sounds, decreased activity, nasal discharge, prostration, and slowed respiration. A minimal mature neutrophilia, evidenced by increased segmented neutrophil numbers, occurred in exposed groups of male and female rats. Exposure to isobutyraldehyde resulted in minimal increases in alanine aminotransferase activity in all groups of male and female rats. Spermatozoal motility in 500 and 1,000 ppm males was significantly reduced and females exposed to 4,000 ppm differed significantly from the chamber control females in the relative time spent in the estrous stages. No gross lesions were observed at necropsy that could be associated with isobutyraldehyde exposure. In the 8,000 ppm groups, severe necrosis of the epithelium, and occasionally of the entire mucosa, of the nasal turbinates accompanied by an acute inflammatory reaction was observed. Increased incidences of squamous metaplasia and mild acute inflammation occurred in male and female rats exposed to 4,000 ppm. Minimal to mild degeneration of the olfactory epithelium was observed in all male rats in the 2,000 and 4,000 ppm groups. Male rats exposed to 4,000 or 8,000 ppm and females exposed to 4,000 ppm had mild osteodystrophy of the turbinate bone. The incidences of necrosis/degeneration of the larynx and trachea were increased in male rats in the 8,000 ppm group. The incidences of mild to moderate lymphoid depletion of the spleen and thymus and lymphoid necrosis of the thymus were significantly increased in male and female rats exposed to 8,000 ppm. 13-WEEK STUDY IN MICE: Ten male and 10 female B6C3F1 mice were exposed to 0, 500, 1,000, 2,000, 4,000, or 8,000 ppm isobutyraldehyde by inhalation, 6 hours per day, 5 days per week, for 13 weeks. One male in the chamber control group, one male in the 1,000 ppm group, nine males and all females in the 4,000 ppm groups, and all males and females in the 8,000 ppm groups died before the end of the study. The final mean body weight and body weight gain of female mice in the 1,000 ppm group were significantly less than those of the chamber controls. Clinical findal findings included decreased activity, tremors, prostration, and slower and labored respiration. The absolute and relative kidney weights of males in the 1,000 and 2,000 ppm groups were significantly increased. There were no gross lesions observed at necropsy that could be associated with isobutyraldehyde exposure. Histopathologically, the nasal cavity and lymphopoietic tissues were considered target organs, with changes similar, but not identical, to those observed in rats. Increased incidences of nonneoplastic lesions of the nasal cavity were observed in male and female mice exposed to 1,000 ppm or greater. These lesions included necrosis, inflammation, hyperplasia, and squamous metaplasia of the epithelium; serous and suppurative exudate within the nasal passages; olfactory epithelial degeneration; and osteodystrophy of the turbinate bone. Mild to moderate lymphoid depletion and/or lymphoid necrosis were observed in the thymus of male and female mice exposed to 8,000 ppm. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female F344/N rats were exposed to 0, 500, 1,000, or 2,000 ppm isobutyraldehyde by inhalation, 6 hours per day, 5 days per week, for 105 weeks Survival, Body Weights, and Clinical Findings No differences in survival rates between exposed and chamber control rats were found. The mean body weights of male and female rats were generally similar to those of the chamber controls throughout the study. Pathology Findings No increase in neoplasm incidences that could be attributed to exposure to isobutyraldehyde was observed in male or female rats. Nonneoplastic lesions related to isobutyraldehyde exposure were limited to the nose and consisted of squamous metaplasia of the respiratory epithelium, degeneration of the olfactory epithelium, and suppurative inflammation. Incidences of minimal to mild squamous metaplasia in 1,000 and 2,000 ppm males and females and in 500 ppm females were significantly greater than those in the chamber controls. Another lesion associated with isobutyraldehyde exposure was minimal to mild degeneration of the olfactory epithelium in 2,000 ppm males and females. The incidences of suppurative inflammation (rhinitis) in male and female rats exposed to 2,000 ppm were increased compared to the chamber controls. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female B6C3F1 mice were exposed to 0, 500, 1,000, or 2,000 ppm isobutyraldehyde by inhalation, 6 hours per day, 5 days per week, for 105 weeks. Survival, Body Weights, and Clinical Findings There was an exposure-related decrease in survival of male mice, and the survival of males exposed to 2,000 ppm was marginally lower than that of the chamber controls. The mean body weights of female mice exposed to 1,000 or 2,000 ppm were lower than those of the chamber controls during the second year of the study. Pathology Findings No neoplasms that could be attributed to iso butyraldehyde exposure were observed in mice. Non neoplastic lesions related to isobutyraldehyde exposure were limited to the nose. The incidences of olfactory epithelial degeneration in 1,000 and 2,000 ppm males and females were significantly greater than in the chamber controls. GENETIC TOXICOLOGY: Isobutyraldehyde is mutagenic in vitro and in vivo, with the strongest responses observed in mammalian cell assays that measured chromosomal damage. Results of an initial mutagenicity test in S. typhimurium were negative; a second test, con ducted with different strains and varying concentrations of induced S9 activation enzymes, gave equivocal results. Strongly positive responses were obtained in the mouse lymphoma assay for mutation induction in L5178Y cells without S9 and in cytogenetic tests for induction of sister chromatid exchanges and chromosomal aberrations in cultured Chinese hamster ovary cells. Sister chromatid exchanges were significantly increased with and without S9, but induction of chromosomal aberrations was noted unequivocally only in the absence of S9. No induction of sex-linked recessive lethal mutations was observed in germ cells of male D. melanogaster administered isobutyraldehyde by feeding or by injection. In vivo, isobutyraldehyde was demonstrated to induce chromosomal aberrations in bone marrow cells of male mice, but no increases in micronuclei were observed in bone marrow cells of mice or rats after administration of isobutyraldehyde. All these in vivo cytogenetic studies used doses that reached lethality CONCLUSIONS: Under the conditions of these 2-year inhalation studies, there was no evidence of carcinogenic activity of isobutyraldehyde in male or female F344/N rats or male or female B6C3F1 mice exposed to 500, 1,000, or 2,000 ppm isobutyraldehyde. In male and female rats, exposure to isobutyraldehyde induced squamous metaplasia and suppurative inflammation of the nasal respiratory epithelium and degeneration of the nasal olfactory epithelium. In male and female mice, exposure to isobutyraldehyde caused degeneration of the nasal olfactory epithelium. Synonyms: Dimethylacetaldehyde; 2-formylpropane; isobutanal; isobutylcarboxaldehyde; isobutyral; isobutyric aldehyde; isobutyrylaldehyde; isopropylformaldehyde; 2-methylpropanal; 2-methyl-1-propanal; a-methylpropionaldehyde; 2-methylpropionaldehyde; valine aldehyde
异丁醛是一种支链烷基醛,用作化学中间体和调味剂。它由美国国家癌症研究所提名,由美国国家毒理学计划(NTP)进行毒性和致癌性研究。提名并选择异丁醛进行研究的原因包括:其产量高表明人类接触的可能性很大;它作为化学中间体和食品调味剂的用途;由于一家醛类制造工厂中工人接触多种醛类后癌症发病率增加,怀疑其具有致癌性;它与甲醛(大鼠鼻腔致癌物)的结构关系;以及缺乏对异丁醛在动物体内的毒性和致癌性研究。虽然人类可通过口服、皮肤接触或吸入接触异丁醛,但由于异丁醛在水和饲料中不稳定,这些动物研究选择了吸入接触途径。雄性和雌性F344/N大鼠以及B6C3F1小鼠通过吸入接触约99%纯的异丁醛,为期13周或2年。在鼠伤寒沙门氏菌、L5178Y小鼠淋巴瘤细胞和培养的中国仓鼠卵巢细胞中进行了体外遗传毒理学研究;在果蝇生殖细胞以及大鼠和小鼠的骨髓细胞中进行了体内试验。
大鼠13周研究:将10只雄性和10只雌性F344/N大鼠分为几组,通过吸入接触0、500、1000、2000、4000或8000 ppm的异丁醛,每天6小时,每周5天,持续13周。所有接触8000 ppm异丁醛的大鼠在研究结束前死亡。4000 ppm组的3只雄性大鼠和6只雌性大鼠以及500 ppm组的1只雌性大鼠在研究结束前死亡。4000 ppm组雄性大鼠的最终平均体重以及4000 ppm组雄性和雌性大鼠的体重增加量显著低于舱内对照组。接触4000或8000 ppm异丁醛的大鼠的临床症状包括呼吸音异常、活动减少、鼻分泌物、虚脱和呼吸减慢。在接触异丁醛的雄性和雌性大鼠组中,出现了以分叶中性粒细胞数量增加为证据的轻微成熟中性粒细胞增多。接触异丁醛导致所有雄性和雌性大鼠组的丙氨酸转氨酶活性略有增加。500和1000 ppm组雄性大鼠的精子活力显著降低,接触4000 ppm异丁醛的雌性大鼠在发情期所花费的相对时间与舱内对照雌性大鼠有显著差异。尸检时未观察到与异丁醛接触相关的肉眼可见病变。在8000 ppm组中,观察到鼻甲上皮严重坏死,偶尔整个黏膜坏死,并伴有急性炎症反应。接触4000 ppm异丁醛的雄性和雌性大鼠中,鳞状化生和轻度急性炎症的发生率增加。在2000和4000 ppm组的所有雄性大鼠中观察到嗅觉上皮有轻微至轻度变性。接触4000或8000 ppm异丁醛的雄性大鼠以及接触4000 ppm异丁醛 的雌性大鼠有鼻甲骨轻度骨营养不良。8000 ppm组雄性大鼠的喉和气管坏死/变性发生率增加。接触8000 ppm异丁醛的雄性和雌性大鼠中,脾脏和胸腺轻度至中度淋巴细胞减少以及胸腺淋巴细胞坏死的发生率显著增加。
小鼠13周研究:将10只雄性和10只雌性B6C3F1小鼠分为几组,通过吸入接触0、500、1000、2000、4000或8000 ppm的异丁醛,每天6小时,每周5天,持续13周。舱内对照组的1只雄性小鼠、1000 ppm组的1只雄性小鼠、4000 ppm组的9只雄性小鼠和所有雌性小鼠以及8000 ppm组的所有雄性和雌性小鼠在研究结束前死亡。1000 ppm组雌性小鼠的最终平均体重和体重增加量显著低于舱内对照组。临床症状包括活动减少、震颤、虚脱以及呼吸减慢和费力。1000和2000 ppm组雄性小鼠的绝对和相对肾脏重量显著增加。尸检时未观察到与异丁醛接触相关的肉眼可见病变。组织病理学上,鼻腔和淋巴造血组织被认为是靶器官,其变化与在大鼠中观察到的相似但不完全相同。接触1000 ppm或更高浓度异丁醛的雄性和雌性小鼠鼻腔非肿瘤性病变的发生率增加。这些病变包括上皮坏死、炎症、增生和鳞状化生;鼻道内浆液性和脓性渗出物;嗅觉上皮变性;以及鼻甲骨骨营养不良。接触~ 8000 ppm异丁醛的雄性和雌性小鼠的胸腺出现轻度至中度淋巴细胞减少和/或淋巴细胞坏死。
将50只雄性和50只雌性F344/N大鼠分为几组,通过吸入接触0、500、 {1,000} {或} {2,000} ppm的异丁醛,每天6小时,每周5天,持续105周。
存活、体重和临床症状
未发现接触组大鼠和舱内对照大鼠的存活率有差异。在整个研究过程中,雄性和雌性大鼠的平均体重通常与舱内对照组相似。
病理学发现
未观察到可归因于接触异丁醛的肿瘤发生率增加。与异丁醛接触相关的非肿瘤性病变仅限于鼻子,包括呼吸上皮的鳞状化生、嗅觉上皮的变性和化脓性炎症。1000和2000 ppm组的雄性和雌性以及500 ppm组的雌性中,轻度至中度鳞状化生的发生率显著高于舱内对照组。与异丁醛接触相关的另一个病变是2000 ppm组的雄性和雌性中嗅觉上皮有轻微至轻度变性。与舱内对照组相比,接触2000 ppm异丁醛的雄性和雌性大鼠中化脓性炎症(鼻炎)的发生率增加。
将50只雄性和50只雌性B6C3F1小鼠分为几组,通过吸入接触0、500、1000或2000 ppm的异丁醛,每天6小时,每周5天,持续105周。
存活、体重和临床症状
雄性小鼠的存活率与接触有关而降低,接触2000 ppm异丁醛的雄性小鼠的存活率略低于舱内对照组。在研究的第二年,接触1000或2000 ppm异丁醛的雌性小鼠的平均体重低于舱内对照组。
病理学发现
未在小鼠中观察到可归因于异丁醛接触的肿瘤。与异丁醛接触相关的非肿瘤性病变仅限于鼻子。1000和2000 ppm组的雄性和雌性中嗅觉上皮变性的发生率显著高于舱内对照组。
异丁醛在体外和体内具有致突变性,在测量染色体损伤的哺乳动物细胞试验中观察到最强的反应。在鼠伤寒沙门氏菌中的初步致突变性试验结果为阴性;用不同菌株和不同浓度的诱导S9激活酶进行的第二次试验结果不明确。在L5178Y细胞的小鼠淋巴瘤试验中,在无S9的情况下诱导突变以及在培养的中国仓鼠卵巢细胞的细胞遗传学试验中诱导姐妹染色单体交换和染色体畸变均获得强阳性反应。无论有无S9,姐妹染色单体交换均显著增加,但仅在无S9时明确观察到染色体畸变的诱导。通过喂食或注射给雄性果蝇生殖细胞施用异丁醛后,未观察到性连锁隐性致死突变的诱导。在体内,异丁醛被证明可诱导雄性小鼠骨髓细胞中的染色体畸变,但在给小鼠或大鼠施用异丁醛后,未观察到骨髓细胞中的微核增加。所有这些体内细胞遗传学研究使用的剂量均达到致死剂量。
在这些为期两年的吸入研究条件下,未发现接触5 {00} {、} {1,} {000} {或} {2,} {000} ppm异丁醛的雄性或雌性F344/N大鼠或雄性或雌性B6C3F1小鼠中有异丁醛致癌活性的证据。在雄性和雌性大鼠中,接触异丁醛会诱导鼻呼吸上皮的鳞状化生和化脓性炎症以及鼻嗅觉上皮的变性。在雄性和雌性小鼠中,接触异丁醛会导致鼻嗅觉上皮的变性。
二甲基乙醛;2 - 甲酰丙烷;异丁醛;异丁基甲醛;异丁酰;异丁酸醛;异丁酰醛;异丙基甲醛;2 - 甲基丙醛;2 - 甲基 - 1 - 丙醛;α - 甲基丙醛;2 - 甲基丙醛;缬氨酸醛