二水重铬酸钠(CAS No. 7789-12-0)对雄性和雌性F344/N大鼠和B6C3F1小鼠以及雄性BALB/c和am3-C57BL/6小鼠的毒性研究。

Toxicity report series Pub Date : 2007-01-01
John R Bucher
{"title":"二水重铬酸钠(CAS No. 7789-12-0)对雄性和雌性F344/N大鼠和B6C3F1小鼠以及雄性BALB/c和am3-C57BL/6小鼠的毒性研究。","authors":"John R Bucher","doi":"","DOIUrl":null,"url":null,"abstract":"<p><p>Sodium dichromate dihydrate is one of a number of inorganic compounds containing hexavalent chromium (CR VI) found in drinking water supplies as a contaminant resulting from various industrial processes including electroplating operations, leather tanning, and textile manufacturing. Because of the lack of adequate experimental data on the toxicity and carcinogenicity of hexavalent chromium ingested orally, and because hexavalent chromium has been found in human drinking water supplies, the California Congressional delegation and the California Environmental Protection Agency nominated hexavalent chromium to the NTP for study. In study 1, male and female F344/N rats and B6C3F1 mice were exposed to sodium dichromate dihydrate (greater than 99% pure) in drinking water for 3 months. In study 2, sodium dichromate dihydrate was administered in drinking water to male B6C3F1, BALB/c, and am3-C57BL/6 mice for 3 months. Genetic toxicology studies were conducted in Salmonella typhimurium, Escherichia coli, and mouse peripheral blood erythrocytes. In study 1, groups of 10 male and 10 female F344/N rats and B6C3F1 mice were given drinking water containing 0, 62.5, 125, 250, 500, or 1,000 mg sodium dichromate dihydrate/L for 3 months (equivalent to average daily doses of approximately 5, 10, 17, 32, or 60 mg sodium dichromate dihydrate/kg body weight to rats and 9, 15, 26, 45, or 80 mg/kg to mice). On a molecular weight basis, these doses are equivalent to approximately 1.7, 3.5, 5.9, 11.2, and 20.9 mg hexavalent chromium/kg body weight per day to rats and 3.1, 5.2, 9.1, 15.7, and 27.9 mg/kg per day to mice. Additional groups of 10 rats per sex were exposed to the same concentrations of sodium dichromate dihydrate for 4 weeks. All rats and mice survived to the end of the study. Reduced body weights occurred in 500 and 1,000 mg/L male rats, 1,000 mg/L female rats, and in male and female mice exposed to 125 mg/L or greater. Water consumption by male and female rats exposed to 250 mg/L or greater and male and female mice exposed to 125 mg/L or greater was generally less than that by the control groups, and decreases in urine volume and increases in urine specific gravity in rats were related to reduced water consumption. Exposure to sodium dichromate dihydrate caused a microcytic hypochromic anemia in rats and mice, but the severity was less in mice. Serum cholesterol and triglyceride concentrations were decreased in rats. Increased bile acid concentrations in exposed groups of rats may have been due to altered hepatic function. The incidences of histiocytic cellular infiltration were generally significantly increased in the duodenum of rats and mice, the liver of female rats, and the mesenteric lymph node of mice exposed to 125 mg/L or greater. Significantly increased nonneoplastic lesions (focal ulceration, regenerative epithelial hyperplasia, and squamous epithelial metaplasia) occurred in the glandular stomach of male and female rats exposed to 1,000 mg/L. Incidences of epithelial hyperplasia of the duodenum were significantly increased in all exposed groups of mice. In study 2, sodium dichromate dihydrate was administered in drinking water to groups of 10 male B6C3F1, 10 male BALB/c, and five male am3-C57BL/6 mice for 3 months at exposure concentrations of 0, 62.5, 125, or 250 mg/L (equivalent to average daily doses of approximately 8, 15, or 25 mg/kg sodium dichromate dihydrate or 2.8, 5.2, or 8.7 mg/kg chromium to B6C3F1, BALB/c, and am3-C57BL/6 mice). All mice in study 2 survived until study termination. Mean body weights of 125 and 250 mg/L B6C3F1 and BALB/c mice and all exposed groups of am3-C57BL/6 mice were less than those of the control groups. Mice exposed to 250 mg/L consumed less water than the control groups. Exposure concentration-related decreases in mean red cell volumes and mean red cell hemoglobin values were observed in all three mouse strains. Erythrocyte counts were increased in exposed B6C3F1 and BALB/c mice but not in am3-C57BL/6 mice. Changes in organ weights were generally consistent with reduced body weights in exposed groups in all mouse strains. No biologically significant differences in reproductive parameters were observed in any strain. Histiocytic cellular infiltration and epithelial hyperplasia of the duodenum occurred in most mice exposed to 125 or 250 mg/L, and the incidences of these lesions were increased in the 62.5 mg/L group compared to controls. Secretory depletion was present in the pancreas of most mice exposed to 125 or 250 mg/L. The incidences of glycogen depletion of the liver were significantly increased in male B6C3F1 mice exposed to 125 or 250 mg/L and in all exposed groups of male am3-C57BL/6 mice. The incidence of histiocytic cellular infiltration in the mesenteric lymph node was significantly increased in the 250 mg/L group of male am3-C57BL/6 mice. Sodium dichromate dihydrate was mutagenic in S. typhimurium strains TA100 and TA98 and in E. coli strain WP2 uvrA pKM101 with and without induced rat liver S9 enzymes. The results of four micronucleus tests conducted in the three strains of mice from studies 1 and 2 were mixed. In study 1, no significant increases were seen in micronucleated normochromatic erythrocytes in peripheral blood samples from male or female B6C3F1 mice; there was a decrease in the percentage of polychromatic erythrocytes among total erythrocytes (an indication of bone marrow toxicity), but the changes were small and not well correlated with exposure concentrations. In study 2, a significant exposure concentration-related increase (P<0.001) in micronucleated normochromatic erythrocytes was seen in am3-C57BL/6 male mice. An equivocal increase in micronucleated erythrocytes was noted in male B6C3F1 mice, based on a small increase in micronucleated normochromatic erythrocytes that did not reach statistical significance. No increase in micronucleated normochromatic erythrocytes was observed in male BALB/c mice. No significant effect of sodium dichromate dihydrate exposure on the percentage of polychromatic erythrocytes was observed in any of the three micronucleus tests conducted in study 2. In summary, administration of sodium dichromate dihydrate in the drinking water to F344/N rats and B6C3F1 mice resulted in focal ulceration, hyperplasia, and metaplasia in the glandular stomach at the limiting ridge in rats in the 1,000 mg/L group and evidence of increased histiocytic infiltration in the liver (female), duodenum of the small intestine, and/or pancreatic lymph nodes at concentrations as low as 62.5 mg/L, the lowest concentration studied. In addition, a microcytic, hypochromic anemia occurred at all exposure concentrations and was considered evidence of a toxic response resulting from absorption of Cr VI following oral ingestion in rats. A similar, but less severe, anemia was evident in mice receiving drinking water containing sodium dichromate dihydrate; histiocytic infiltration was noted in the duodenum of all three strains studied (B6C3F1, BALB/c, and am3-C57BL/6) at all concentrations employed, in the mesenteric lymph nodes at 125 mg/L or greater in the B6C3F1 strain, and at 250 mg/L in the am3-C57BL/6 strain. There was no consistent evidence of hepatocyte injury in mice in any of the strains tested. Variations in glycogen content were considered more likely related to diminished food intake than to the toxicity of sodium dichromate dihydrate. Synonyms: Chromic acid; dichromic acid; disodium salt, dihydrate; disodium dichromate dihydrate; chromium VI.</p>","PeriodicalId":23116,"journal":{"name":"Toxicity report series","volume":" 72","pages":"1-G4"},"PeriodicalIF":0.0000,"publicationDate":"2007-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"NTP toxicity studies of sodium dichromate dihydrate (CAS No. 7789-12-0) administered in drinking water to male and female F344/N rats and B6C3F1 mice and male BALB/c and am3-C57BL/6 mice.\",\"authors\":\"John R Bucher\",\"doi\":\"\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p><p>Sodium dichromate dihydrate is one of a number of inorganic compounds containing hexavalent chromium (CR VI) found in drinking water supplies as a contaminant resulting from various industrial processes including electroplating operations, leather tanning, and textile manufacturing. Because of the lack of adequate experimental data on the toxicity and carcinogenicity of hexavalent chromium ingested orally, and because hexavalent chromium has been found in human drinking water supplies, the California Congressional delegation and the California Environmental Protection Agency nominated hexavalent chromium to the NTP for study. In study 1, male and female F344/N rats and B6C3F1 mice were exposed to sodium dichromate dihydrate (greater than 99% pure) in drinking water for 3 months. In study 2, sodium dichromate dihydrate was administered in drinking water to male B6C3F1, BALB/c, and am3-C57BL/6 mice for 3 months. Genetic toxicology studies were conducted in Salmonella typhimurium, Escherichia coli, and mouse peripheral blood erythrocytes. In study 1, groups of 10 male and 10 female F344/N rats and B6C3F1 mice were given drinking water containing 0, 62.5, 125, 250, 500, or 1,000 mg sodium dichromate dihydrate/L for 3 months (equivalent to average daily doses of approximately 5, 10, 17, 32, or 60 mg sodium dichromate dihydrate/kg body weight to rats and 9, 15, 26, 45, or 80 mg/kg to mice). On a molecular weight basis, these doses are equivalent to approximately 1.7, 3.5, 5.9, 11.2, and 20.9 mg hexavalent chromium/kg body weight per day to rats and 3.1, 5.2, 9.1, 15.7, and 27.9 mg/kg per day to mice. Additional groups of 10 rats per sex were exposed to the same concentrations of sodium dichromate dihydrate for 4 weeks. All rats and mice survived to the end of the study. Reduced body weights occurred in 500 and 1,000 mg/L male rats, 1,000 mg/L female rats, and in male and female mice exposed to 125 mg/L or greater. Water consumption by male and female rats exposed to 250 mg/L or greater and male and female mice exposed to 125 mg/L or greater was generally less than that by the control groups, and decreases in urine volume and increases in urine specific gravity in rats were related to reduced water consumption. Exposure to sodium dichromate dihydrate caused a microcytic hypochromic anemia in rats and mice, but the severity was less in mice. Serum cholesterol and triglyceride concentrations were decreased in rats. Increased bile acid concentrations in exposed groups of rats may have been due to altered hepatic function. The incidences of histiocytic cellular infiltration were generally significantly increased in the duodenum of rats and mice, the liver of female rats, and the mesenteric lymph node of mice exposed to 125 mg/L or greater. Significantly increased nonneoplastic lesions (focal ulceration, regenerative epithelial hyperplasia, and squamous epithelial metaplasia) occurred in the glandular stomach of male and female rats exposed to 1,000 mg/L. Incidences of epithelial hyperplasia of the duodenum were significantly increased in all exposed groups of mice. In study 2, sodium dichromate dihydrate was administered in drinking water to groups of 10 male B6C3F1, 10 male BALB/c, and five male am3-C57BL/6 mice for 3 months at exposure concentrations of 0, 62.5, 125, or 250 mg/L (equivalent to average daily doses of approximately 8, 15, or 25 mg/kg sodium dichromate dihydrate or 2.8, 5.2, or 8.7 mg/kg chromium to B6C3F1, BALB/c, and am3-C57BL/6 mice). All mice in study 2 survived until study termination. Mean body weights of 125 and 250 mg/L B6C3F1 and BALB/c mice and all exposed groups of am3-C57BL/6 mice were less than those of the control groups. Mice exposed to 250 mg/L consumed less water than the control groups. Exposure concentration-related decreases in mean red cell volumes and mean red cell hemoglobin values were observed in all three mouse strains. Erythrocyte counts were increased in exposed B6C3F1 and BALB/c mice but not in am3-C57BL/6 mice. Changes in organ weights were generally consistent with reduced body weights in exposed groups in all mouse strains. No biologically significant differences in reproductive parameters were observed in any strain. Histiocytic cellular infiltration and epithelial hyperplasia of the duodenum occurred in most mice exposed to 125 or 250 mg/L, and the incidences of these lesions were increased in the 62.5 mg/L group compared to controls. Secretory depletion was present in the pancreas of most mice exposed to 125 or 250 mg/L. The incidences of glycogen depletion of the liver were significantly increased in male B6C3F1 mice exposed to 125 or 250 mg/L and in all exposed groups of male am3-C57BL/6 mice. The incidence of histiocytic cellular infiltration in the mesenteric lymph node was significantly increased in the 250 mg/L group of male am3-C57BL/6 mice. Sodium dichromate dihydrate was mutagenic in S. typhimurium strains TA100 and TA98 and in E. coli strain WP2 uvrA pKM101 with and without induced rat liver S9 enzymes. The results of four micronucleus tests conducted in the three strains of mice from studies 1 and 2 were mixed. In study 1, no significant increases were seen in micronucleated normochromatic erythrocytes in peripheral blood samples from male or female B6C3F1 mice; there was a decrease in the percentage of polychromatic erythrocytes among total erythrocytes (an indication of bone marrow toxicity), but the changes were small and not well correlated with exposure concentrations. In study 2, a significant exposure concentration-related increase (P<0.001) in micronucleated normochromatic erythrocytes was seen in am3-C57BL/6 male mice. An equivocal increase in micronucleated erythrocytes was noted in male B6C3F1 mice, based on a small increase in micronucleated normochromatic erythrocytes that did not reach statistical significance. No increase in micronucleated normochromatic erythrocytes was observed in male BALB/c mice. No significant effect of sodium dichromate dihydrate exposure on the percentage of polychromatic erythrocytes was observed in any of the three micronucleus tests conducted in study 2. In summary, administration of sodium dichromate dihydrate in the drinking water to F344/N rats and B6C3F1 mice resulted in focal ulceration, hyperplasia, and metaplasia in the glandular stomach at the limiting ridge in rats in the 1,000 mg/L group and evidence of increased histiocytic infiltration in the liver (female), duodenum of the small intestine, and/or pancreatic lymph nodes at concentrations as low as 62.5 mg/L, the lowest concentration studied. In addition, a microcytic, hypochromic anemia occurred at all exposure concentrations and was considered evidence of a toxic response resulting from absorption of Cr VI following oral ingestion in rats. A similar, but less severe, anemia was evident in mice receiving drinking water containing sodium dichromate dihydrate; histiocytic infiltration was noted in the duodenum of all three strains studied (B6C3F1, BALB/c, and am3-C57BL/6) at all concentrations employed, in the mesenteric lymph nodes at 125 mg/L or greater in the B6C3F1 strain, and at 250 mg/L in the am3-C57BL/6 strain. There was no consistent evidence of hepatocyte injury in mice in any of the strains tested. Variations in glycogen content were considered more likely related to diminished food intake than to the toxicity of sodium dichromate dihydrate. Synonyms: Chromic acid; dichromic acid; disodium salt, dihydrate; disodium dichromate dihydrate; chromium VI.</p>\",\"PeriodicalId\":23116,\"journal\":{\"name\":\"Toxicity report series\",\"volume\":\" 72\",\"pages\":\"1-G4\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"2007-01-01\",\"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}","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}
引用次数: 0

摘要

二水合重铬酸钠是饮用水中含有六价铬(CR VI)的众多无机化合物之一,是各种工业过程(包括电镀操作、皮革鞣制和纺织制造)产生的污染物。由于缺乏关于口服六价铬的毒性和致癌性的充分实验数据,并且由于在人类饮用水供应中发现了六价铬,加州国会代表团和加州环境保护局向国家毒毒局提名六价铬进行研究。在研究1中,雄性和雌性F344/N大鼠和B6C3F1小鼠在饮用水中暴露于重铬酸钠(纯度大于99%)3个月。在研究2中,雄性B6C3F1、BALB/c和am3-C57BL/6小鼠连续3个月以饮用水形式给予二水重铬酸钠。鼠伤寒沙门菌、大肠杆菌和小鼠外周血进行了遗传毒理学研究。在研究1中,每组10只雄性和10只雌性F344/N大鼠和B6C3F1小鼠连续3个月饮用含有0、62.5、125、250、500或1000 mg二水重铬酸钠/L的水(相当于大鼠的平均日剂量约为5、10、17、32或60 mg二水重铬酸钠/kg体重,小鼠的平均日剂量为9、15、26、45或80 mg/kg)。以分子量为基础,这些剂量相当于大鼠每天每公斤体重约1.7、3.5、5.9、11.2和20.9毫克六价铬,小鼠每天约3.1、5.2、9.1、15.7和27.9毫克六价铬。另一组每性别10只的大鼠暴露在相同浓度的二水重铬酸钠中4周。所有的大鼠和小鼠都活到了研究结束。500mg /L和1000mg /L的雄性大鼠、1000mg /L的雌性大鼠以及125mg /L或更高浓度的雄性和雌性小鼠的体重都有所减轻。暴露于250 mg/L及以上的雄性和雌性大鼠和暴露于125 mg/L及以上的雄性和雌性小鼠的饮水量普遍低于对照组,大鼠尿量减少和尿比重增加与饮水量减少有关。暴露于二水重铬酸钠可引起大鼠和小鼠的小细胞性低色素贫血,但小鼠的严重程度较轻。大鼠血清胆固醇和甘油三酯浓度降低。暴露组大鼠胆汁酸浓度升高可能是由于肝功能改变所致。暴露于125 mg/L及以上的大鼠、小鼠十二指肠、雌性大鼠肝脏、小鼠肠系膜淋巴结组织细胞浸润发生率普遍显著增加。暴露于1000mg /L的雄性和雌性大鼠腺胃非肿瘤性病变(局灶性溃疡、再生上皮增生和鳞状上皮化生)显著增加。各暴露组小鼠十二指肠上皮增生发生率均显著升高。在研究2中,以饮用水形式给10只雄性B6C3F1、10只雄性BALB/c和5只雄性am3-C57BL/6小鼠,以0、62.5、125或250 mg/L的暴露浓度(相当于平均日剂量约为8、15或25 mg/kg二水重铬酸钠或2.8、5.2或8.7 mg/kg铬给B6C3F1、BALB/c和am3-C57BL/6小鼠),持续3个月。研究2中的所有小鼠都存活到研究结束。125和250 mg/L B6C3F1和BALB/c小鼠及am3-C57BL/6暴露组小鼠的平均体重均小于对照组。暴露于250毫克/升的小鼠比对照组消耗更少的水。在所有三种小鼠品系中均观察到暴露浓度相关的平均红细胞体积和平均红细胞血红蛋白值的降低。暴露的B6C3F1和BALB/c小鼠红细胞计数增加,而am3-C57BL/6小鼠红细胞计数没有增加。在所有小鼠品系中,暴露组的器官重量变化大体上与体重减轻一致。在任何品系中均未观察到生殖参数的生物学显著差异。暴露于125或250 mg/L的大多数小鼠发生组织细胞浸润和十二指肠上皮增生,与对照组相比,62.5 mg/L组这些病变的发生率增加。暴露于125或250 mg/L的大多数小鼠胰腺中存在分泌耗损。暴露于125或250 mg/L的雄性B6C3F1小鼠和所有暴露组的雄性am3-C57BL/6小鼠肝脏糖原消耗发生率均显著增加。250 mg/L雄性am3-C57BL/6小鼠肠系膜淋巴结组织细胞浸润发生率显著升高。二水合重铬酸钠对鼠伤寒沙门氏菌TA100和TA98具有诱变作用。 大肠杆菌菌株WP2 uvrA pKM101诱导和不诱导大鼠肝脏S9酶。在研究1和研究2的三种小鼠品系中进行的四次微核试验结果是混合的。在研究1中,雄性或雌性B6C3F1小鼠外周血样本中微核正染色红细胞未见显著增加;红细胞中多染红细胞的百分比有所下降(骨髓毒性的一个指标),但变化很小,与暴露浓度没有很好的相关性。在研究2中,暴露浓度相关的显著增加(P
本文章由计算机程序翻译,如有差异,请以英文原文为准。
NTP toxicity studies of sodium dichromate dihydrate (CAS No. 7789-12-0) administered in drinking water to male and female F344/N rats and B6C3F1 mice and male BALB/c and am3-C57BL/6 mice.

Sodium dichromate dihydrate is one of a number of inorganic compounds containing hexavalent chromium (CR VI) found in drinking water supplies as a contaminant resulting from various industrial processes including electroplating operations, leather tanning, and textile manufacturing. Because of the lack of adequate experimental data on the toxicity and carcinogenicity of hexavalent chromium ingested orally, and because hexavalent chromium has been found in human drinking water supplies, the California Congressional delegation and the California Environmental Protection Agency nominated hexavalent chromium to the NTP for study. In study 1, male and female F344/N rats and B6C3F1 mice were exposed to sodium dichromate dihydrate (greater than 99% pure) in drinking water for 3 months. In study 2, sodium dichromate dihydrate was administered in drinking water to male B6C3F1, BALB/c, and am3-C57BL/6 mice for 3 months. Genetic toxicology studies were conducted in Salmonella typhimurium, Escherichia coli, and mouse peripheral blood erythrocytes. In study 1, groups of 10 male and 10 female F344/N rats and B6C3F1 mice were given drinking water containing 0, 62.5, 125, 250, 500, or 1,000 mg sodium dichromate dihydrate/L for 3 months (equivalent to average daily doses of approximately 5, 10, 17, 32, or 60 mg sodium dichromate dihydrate/kg body weight to rats and 9, 15, 26, 45, or 80 mg/kg to mice). On a molecular weight basis, these doses are equivalent to approximately 1.7, 3.5, 5.9, 11.2, and 20.9 mg hexavalent chromium/kg body weight per day to rats and 3.1, 5.2, 9.1, 15.7, and 27.9 mg/kg per day to mice. Additional groups of 10 rats per sex were exposed to the same concentrations of sodium dichromate dihydrate for 4 weeks. All rats and mice survived to the end of the study. Reduced body weights occurred in 500 and 1,000 mg/L male rats, 1,000 mg/L female rats, and in male and female mice exposed to 125 mg/L or greater. Water consumption by male and female rats exposed to 250 mg/L or greater and male and female mice exposed to 125 mg/L or greater was generally less than that by the control groups, and decreases in urine volume and increases in urine specific gravity in rats were related to reduced water consumption. Exposure to sodium dichromate dihydrate caused a microcytic hypochromic anemia in rats and mice, but the severity was less in mice. Serum cholesterol and triglyceride concentrations were decreased in rats. Increased bile acid concentrations in exposed groups of rats may have been due to altered hepatic function. The incidences of histiocytic cellular infiltration were generally significantly increased in the duodenum of rats and mice, the liver of female rats, and the mesenteric lymph node of mice exposed to 125 mg/L or greater. Significantly increased nonneoplastic lesions (focal ulceration, regenerative epithelial hyperplasia, and squamous epithelial metaplasia) occurred in the glandular stomach of male and female rats exposed to 1,000 mg/L. Incidences of epithelial hyperplasia of the duodenum were significantly increased in all exposed groups of mice. In study 2, sodium dichromate dihydrate was administered in drinking water to groups of 10 male B6C3F1, 10 male BALB/c, and five male am3-C57BL/6 mice for 3 months at exposure concentrations of 0, 62.5, 125, or 250 mg/L (equivalent to average daily doses of approximately 8, 15, or 25 mg/kg sodium dichromate dihydrate or 2.8, 5.2, or 8.7 mg/kg chromium to B6C3F1, BALB/c, and am3-C57BL/6 mice). All mice in study 2 survived until study termination. Mean body weights of 125 and 250 mg/L B6C3F1 and BALB/c mice and all exposed groups of am3-C57BL/6 mice were less than those of the control groups. Mice exposed to 250 mg/L consumed less water than the control groups. Exposure concentration-related decreases in mean red cell volumes and mean red cell hemoglobin values were observed in all three mouse strains. Erythrocyte counts were increased in exposed B6C3F1 and BALB/c mice but not in am3-C57BL/6 mice. Changes in organ weights were generally consistent with reduced body weights in exposed groups in all mouse strains. No biologically significant differences in reproductive parameters were observed in any strain. Histiocytic cellular infiltration and epithelial hyperplasia of the duodenum occurred in most mice exposed to 125 or 250 mg/L, and the incidences of these lesions were increased in the 62.5 mg/L group compared to controls. Secretory depletion was present in the pancreas of most mice exposed to 125 or 250 mg/L. The incidences of glycogen depletion of the liver were significantly increased in male B6C3F1 mice exposed to 125 or 250 mg/L and in all exposed groups of male am3-C57BL/6 mice. The incidence of histiocytic cellular infiltration in the mesenteric lymph node was significantly increased in the 250 mg/L group of male am3-C57BL/6 mice. Sodium dichromate dihydrate was mutagenic in S. typhimurium strains TA100 and TA98 and in E. coli strain WP2 uvrA pKM101 with and without induced rat liver S9 enzymes. The results of four micronucleus tests conducted in the three strains of mice from studies 1 and 2 were mixed. In study 1, no significant increases were seen in micronucleated normochromatic erythrocytes in peripheral blood samples from male or female B6C3F1 mice; there was a decrease in the percentage of polychromatic erythrocytes among total erythrocytes (an indication of bone marrow toxicity), but the changes were small and not well correlated with exposure concentrations. In study 2, a significant exposure concentration-related increase (P<0.001) in micronucleated normochromatic erythrocytes was seen in am3-C57BL/6 male mice. An equivocal increase in micronucleated erythrocytes was noted in male B6C3F1 mice, based on a small increase in micronucleated normochromatic erythrocytes that did not reach statistical significance. No increase in micronucleated normochromatic erythrocytes was observed in male BALB/c mice. No significant effect of sodium dichromate dihydrate exposure on the percentage of polychromatic erythrocytes was observed in any of the three micronucleus tests conducted in study 2. In summary, administration of sodium dichromate dihydrate in the drinking water to F344/N rats and B6C3F1 mice resulted in focal ulceration, hyperplasia, and metaplasia in the glandular stomach at the limiting ridge in rats in the 1,000 mg/L group and evidence of increased histiocytic infiltration in the liver (female), duodenum of the small intestine, and/or pancreatic lymph nodes at concentrations as low as 62.5 mg/L, the lowest concentration studied. In addition, a microcytic, hypochromic anemia occurred at all exposure concentrations and was considered evidence of a toxic response resulting from absorption of Cr VI following oral ingestion in rats. A similar, but less severe, anemia was evident in mice receiving drinking water containing sodium dichromate dihydrate; histiocytic infiltration was noted in the duodenum of all three strains studied (B6C3F1, BALB/c, and am3-C57BL/6) at all concentrations employed, in the mesenteric lymph nodes at 125 mg/L or greater in the B6C3F1 strain, and at 250 mg/L in the am3-C57BL/6 strain. There was no consistent evidence of hepatocyte injury in mice in any of the strains tested. Variations in glycogen content were considered more likely related to diminished food intake than to the toxicity of sodium dichromate dihydrate. Synonyms: Chromic acid; dichromic acid; disodium salt, dihydrate; disodium dichromate dihydrate; chromium VI.

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