NTP technical report on the toxicity studies of Glutaraldehyde (CAS No. 111-30-8) Adminstered by Inhalation to F344/N Rats and B6C3F1 Mice.

Toxicity report series Pub Date : 1993-03-01
Frank Kari
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The ability of glutaraldehyde to induce sex-linked recessive lethal mutations was also studied in vivo in Drosophila melanogaster. In 2-week inhalation studies, groups of five rats and five mice of each sex were exposed to glutaraldehyde by whole-body inhalation at concentrations of 0, 0.16, 0.5, 1.6, 5, and 16 ppm for 6 hours per day, 5 days per week. All rats and mice exposed to 5 or 16 ppm glutaraldehyde died before the end of the studies; all mice exposed to 1.6 ppm also died. Rats exposed to 1.6 ppm did not gain weight. Deaths were attributed to severe respiratory distress. Mice appeared to be more sensitive than rats because the small airways of the nasal passage of mice were more easily blocked by cell debris and keratin. Lesions noted in the nasal passage and larynx of rats and mice included necrosis, inflammation, and squamous metaplasia. At higher exposure concentrations, similar lesions were present in the trachea of rats and mice and in the lung and on the tongue of rats. In 13-week studies, groups of 10 rats and 10 mice of each sex were exposed to glutaraldehyde by whole-body inhalation at concentrations of 0, 62.5, 125, 250, 500, and 1000 ppb for 6 hours per day, 5 days per week. There were no exposure-related deaths in rats, but all mice exposed to 1000 ppb and two female mice exposed to 500 ppb died before the end of the study. Body weight gains were reduced in male rats exposed to 1000 ppb and in female rats exposed to 500 or 1000 ppb. Body weight gains of male mice exposed to 125, 250, or 500 ppb and female mice exposed to 250 or 500 ppb were reduced in a concentration-related manner. There was no clear evidence of systemic toxicity in rats or mice by histopathologic or clinical pathology assessments; however, exposure-related lesions in the respiratory tract were observed, and resembled those noted in the 2-week studies. In rats, the most severe lesions occurred in the anterior portions of the nasal passages and involved both the respiratory and olfactory epithelium. Hyperplasia and squamous metaplasia were most commonly noted on the lateral wall of the nasal cavity and on the tips of the nasoturbinates. Lesions were most extensive in rats exposed to 1000 ppb, but were also noted in the 250 and 500 ppb groups and in one male exposed to 125 ppb. In mice, histopathologic lesions in the respiratory tract were most severe in animals in the 1000 ppb group and consisted of minimal to mild squamous metaplasia of the laryngeal epithelium, suppurative inflammation in the anterior parts of the nasal cavity, and minimal squamous metaplasia on the tips of the nasoturbinates. Necrosis and inflammation were noted at lower concentrations, primarily in the anterior portion of the nasal passage. In genetic toxicity studies, glutaraldehyde was mutagenic with and without S9 metabolic activation in Salmonella typhimurium strains TA100, TA102, and TA104. Glutaraldehyde was mutagenic in mouse L5178Y lymphoma cells in the absence of S9 and induced sister chromatid exchanges in Chinese hamster ovary cells with and without S9. In one laboratory, chromosomal aberrations were induced in Chinese hamster ovary cells by glutaraldehyde in the absence of S9 only; no increase in chromosomal aberrations was observed with or without S9 in a second laboratory. Glutaraldehyde did not induce sex-linked recessive lethal mutations in germ cells of male Drosophila melanogaster treated as adults by feeding or injection or treated as larvae by feeding. In summary, exposure of rats and mice to glutaraldehyde by inhalation for up to 13 weeks resulted in a spectrum of necrotic, inflammatory, and regenerative lesions confined to the upper respiratory tract. Mice were somewhat more sensitive than rats because the small airways of the nasal passage in mice were more prone to blockage with cellular debris, bacteria, and keratin. The no-observed-adverse-effect level (NOAEL) was 125 ppb for respiratory lesions in rats. An NOAEL was not reached for mice, as inflammation was found in the anterior nasal passage at concentrations as low as 62.5 ppb. Synonyms: 1,5-Pentanedial; glutaral; glutaric dialdehyde; 1,3-diformylpropane.</p>","PeriodicalId":23116,"journal":{"name":"Toxicity report series","volume":"25 ","pages":"1-E10"},"PeriodicalIF":0.0000,"publicationDate":"1993-03-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Toxicity report series","FirstCategoryId":"1085","ListUrlMain":"","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
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Abstract

Glutaraldehyde is a potent sensory irritant with the capability to cross-link, or fix, proteins. It is used industrially as an antimicrobial agent and as a cold sterilant in hospitals, and it has a variety of other industrial uses. The toxicity of glutaraldehyde was evaluated in 2-week and 13-week inhalation exposure studies in F344/N rats and B6C3F1 mice. In addition to histopathology, evaluations included clinical pathology and assessments of sperm morphology and estrous cycle length. In vitro genetic toxicity studies included assessments of mutagenicity in Salmonella typhimurium and in mouse lymphoma L5178Y cells and analysis of chromosomal aberrations and sister chromatid exchanges in Chinese hamster ovary cells. The ability of glutaraldehyde to induce sex-linked recessive lethal mutations was also studied in vivo in Drosophila melanogaster. In 2-week inhalation studies, groups of five rats and five mice of each sex were exposed to glutaraldehyde by whole-body inhalation at concentrations of 0, 0.16, 0.5, 1.6, 5, and 16 ppm for 6 hours per day, 5 days per week. All rats and mice exposed to 5 or 16 ppm glutaraldehyde died before the end of the studies; all mice exposed to 1.6 ppm also died. Rats exposed to 1.6 ppm did not gain weight. Deaths were attributed to severe respiratory distress. Mice appeared to be more sensitive than rats because the small airways of the nasal passage of mice were more easily blocked by cell debris and keratin. Lesions noted in the nasal passage and larynx of rats and mice included necrosis, inflammation, and squamous metaplasia. At higher exposure concentrations, similar lesions were present in the trachea of rats and mice and in the lung and on the tongue of rats. In 13-week studies, groups of 10 rats and 10 mice of each sex were exposed to glutaraldehyde by whole-body inhalation at concentrations of 0, 62.5, 125, 250, 500, and 1000 ppb for 6 hours per day, 5 days per week. There were no exposure-related deaths in rats, but all mice exposed to 1000 ppb and two female mice exposed to 500 ppb died before the end of the study. Body weight gains were reduced in male rats exposed to 1000 ppb and in female rats exposed to 500 or 1000 ppb. Body weight gains of male mice exposed to 125, 250, or 500 ppb and female mice exposed to 250 or 500 ppb were reduced in a concentration-related manner. There was no clear evidence of systemic toxicity in rats or mice by histopathologic or clinical pathology assessments; however, exposure-related lesions in the respiratory tract were observed, and resembled those noted in the 2-week studies. In rats, the most severe lesions occurred in the anterior portions of the nasal passages and involved both the respiratory and olfactory epithelium. Hyperplasia and squamous metaplasia were most commonly noted on the lateral wall of the nasal cavity and on the tips of the nasoturbinates. Lesions were most extensive in rats exposed to 1000 ppb, but were also noted in the 250 and 500 ppb groups and in one male exposed to 125 ppb. In mice, histopathologic lesions in the respiratory tract were most severe in animals in the 1000 ppb group and consisted of minimal to mild squamous metaplasia of the laryngeal epithelium, suppurative inflammation in the anterior parts of the nasal cavity, and minimal squamous metaplasia on the tips of the nasoturbinates. Necrosis and inflammation were noted at lower concentrations, primarily in the anterior portion of the nasal passage. In genetic toxicity studies, glutaraldehyde was mutagenic with and without S9 metabolic activation in Salmonella typhimurium strains TA100, TA102, and TA104. Glutaraldehyde was mutagenic in mouse L5178Y lymphoma cells in the absence of S9 and induced sister chromatid exchanges in Chinese hamster ovary cells with and without S9. In one laboratory, chromosomal aberrations were induced in Chinese hamster ovary cells by glutaraldehyde in the absence of S9 only; no increase in chromosomal aberrations was observed with or without S9 in a second laboratory. Glutaraldehyde did not induce sex-linked recessive lethal mutations in germ cells of male Drosophila melanogaster treated as adults by feeding or injection or treated as larvae by feeding. In summary, exposure of rats and mice to glutaraldehyde by inhalation for up to 13 weeks resulted in a spectrum of necrotic, inflammatory, and regenerative lesions confined to the upper respiratory tract. Mice were somewhat more sensitive than rats because the small airways of the nasal passage in mice were more prone to blockage with cellular debris, bacteria, and keratin. The no-observed-adverse-effect level (NOAEL) was 125 ppb for respiratory lesions in rats. An NOAEL was not reached for mice, as inflammation was found in the anterior nasal passage at concentrations as low as 62.5 ppb. Synonyms: 1,5-Pentanedial; glutaral; glutaric dialdehyde; 1,3-diformylpropane.

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国家毒理学规划关于吸入戊二醛对F344/N大鼠和B6C3F1小鼠毒性研究的技术报告(CAS No. 111-30-8)。
戊二醛是一种强效的感官刺激物,具有交联或固定蛋白质的能力。它在工业上用作抗菌剂和医院的冷消毒剂,并有各种其他工业用途。在F344/N大鼠和B6C3F1小鼠的2周和13周吸入暴露研究中评估戊二醛的毒性。除了组织病理学,评估还包括临床病理学和精子形态和发情周期长度的评估。体外遗传毒性研究包括鼠伤寒沙门菌和小鼠淋巴瘤L5178Y细胞的致突变性评估,以及中国仓鼠卵巢细胞染色体畸变和姐妹染色单体交换分析。我们还研究了戊二醛在黑腹果蝇体内诱导性连锁隐性致死突变的能力。在为期两周的吸入研究中,每组5只大鼠和5只小鼠,每组5只,每周5天,每天6小时,通过全身吸入浓度为0、0.16、0.5、1.6、5和16 ppm的戊二醛。所有暴露于5或16 ppm戊二醛的大鼠和小鼠在研究结束前死亡;所有暴露在PPM浓度为1.6的小鼠也均死亡。暴露在1.6 ppm中的老鼠没有体重增加。死亡原因是严重的呼吸窘迫。小鼠似乎比大鼠更敏感,因为小鼠的鼻腔通道的小气道更容易被细胞碎片和角蛋白堵塞。在大鼠和小鼠的鼻通道和喉部发现的病变包括坏死、炎症和鳞状化生。在较高的暴露浓度下,在大鼠和小鼠的气管、大鼠的肺部和舌头上也出现了类似的损伤。在为期13周的研究中,每组10只大鼠和10只小鼠,每个性别,通过全身吸入浓度为0、62.5、125、250、500和1000 ppb的戊二醛,每天6小时,每周5天。在大鼠中没有与暴露相关的死亡,但所有暴露于1000 ppb的小鼠和两只暴露于500 ppb的雌性小鼠在研究结束前死亡。暴露于1000 ppb的雄性大鼠和暴露于500或1000 ppb的雌性大鼠体重增加减少。暴露于125、250或500 ppb的雄性小鼠和暴露于250或500 ppb的雌性小鼠的体重增加以浓度相关的方式减少。经组织病理学或临床病理学评估,未发现大鼠或小鼠的系统性毒性的明确证据;然而,在呼吸道中观察到与暴露相关的病变,并且与2周研究中注意到的相似。在大鼠中,最严重的病变发生在鼻通道的前部,并累及呼吸和嗅觉上皮。增生和鳞状化生最常见于鼻腔侧壁和鼻鼻甲尖端。在暴露于1000 ppb的大鼠中,病变最广泛,但在250和500 ppb组以及一只暴露于125 ppb的雄性中也发现了病变。在小鼠中,1000 ppb组动物呼吸道的组织病理学病变最严重,包括喉部上皮的轻微至轻度鳞状化生,鼻腔前部的化脓性炎症和鼻鼻甲尖端的轻微鳞状化生。坏死和炎症在较低浓度时被注意到,主要在鼻通道的前部。在遗传毒性研究中,戊二醛对鼠伤寒沙门氏菌菌株TA100、TA102和TA104具有诱变作用,无论是否具有S9代谢激活。戊二醛在不含S9的小鼠L5178Y淋巴瘤细胞中具有诱变作用,在含S9和不含S9的中国仓鼠卵巢细胞中诱导姐妹染色单体交换。在一个实验室中,戊二醛在没有S9的情况下诱导中国仓鼠卵巢细胞染色体畸变;在第二个实验室中,无论有无S9,均未观察到染色体畸变的增加。戊二醛对雄性黑腹果蝇生殖细胞的性连锁隐性致死性突变无诱导作用。总之,大鼠和小鼠吸入戊二醛长达13周,导致上呼吸道的一系列坏死、炎症和再生病变。小鼠比大鼠更敏感,因为小鼠鼻腔通道的小气道更容易被细胞碎片、细菌和角蛋白堵塞。对大鼠呼吸道病变,未观察到的不良反应水平(NOAEL)为125 ppb。小鼠没有达到NOAEL,因为在浓度低至62.5 ppb时,在前鼻通道发现了炎症。同义词:1、5-Pentanedial;glutaral;戊二醛;1, 3-diformylpropane。
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Toxicity studies of acetoin and 2,3-pentanedione administered by inhalation to Wistar Han [Crl:WI(Han)] rats and B6C3F1/N mice. Toxicity studies of sodium metavanadate and vanadyl sulfate administered in drinking water to Sprague Dawley (Hsd:Sprague Dawley SD) rats and B6C3F1/N mice. Toxicity studies of (+)-usnic acid administered in feed to F344/N Nctr rats and B6C3F1/Nctr mice. Toxicity studies of Usnea lichens containing (+/-)-usnic acid administered in feed to F344/N Nctr rats and B6C3F1/Nctr mice. Toxicity studies of trans-resveratrol administered by gavage for two weeks or three months to F344/NTac rats, Wistar Han [Crl:WI(Han)] rats, and B6C3F1/N mice.
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