Showing papers on "Sodium dichromate published in 2007"

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.

Abstract: 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.

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.

Abstract: 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.

Sodium molybdate—a possible alternate additive for sodium dichromate in the electrolytic production of sodium chlorate

Abstract: Sodium dichromate is commonly used in sodium chlorate production to maintain high current efficiency; however, it is also a well documented carcinogen. To reduce the environmental impact, identification of a suitable alternative with similar buffering characteristics to dichromate and without adverse effect on the electrolytic performance of sodium chlorate production is important; sodium molybdate is a good candidate. Molybdate ion and its conjugated acid work as a buffer pair at pH 5–6, a lower and slightly narrower pH window than the typical buffer region of dichromate. Nonetheless, the molybdate buffer works effectively during the electrolytic process by maintaining pH at 5.9. Although the use of molybdate buffer will lower the overpotential of hydrogen evolution reaction (HER) by 100 mV, the average off-gas oxygen content is noticeably compromised at 3.6–4.6%, measured using a pilot cell operated at 3 kA m−2and 80 °C during a 3-day trial. The resulting current efficiency of 91 92% is significantly lower than when dichromate is employed as the process additive (> 96%). Mixtures of different dichromate and molybdate ratio were also investigated in terms of the resulting cathode surface potential.

Medicinal methylene blue synthesis method

Abstract: The invention discloses a synthesizing method of medicinal methylen blue, which is characterized by the following: adopting N, N-dimethyl p-phenylene diamine hydrochlorate as raw material; obtaining 2-amino-5-dimethyl amino phenyl thiosulfonic acid oxidized by sodium dichromate and substituted by natrium thiosulfuricum; condensing with N, N-dimethyl p-phenylene diamine to obtain methylen blue zinc chloride salt oxidized by magnesium dioxide; neutralizing methylen blue zinc chloride salt through sodium carbonate to obtain methylen blue.

Macrokinetic Study of the Electrochemical Synthesis Process of Sodium Dichromate

Abstract: In order to address the problems existing in the traditional production techniques for sodium dichromate, a new green technology for producing sodium dichromate using an electrochemical synthesis method was studied. Using a self-made electrosynthesis reactor composed of pure titanium and stainless steel, with a multiple-unit metal oxide combination anode, a stainless steel cathode, and a reinforcing combination cation exchange membrane, the kinetic experiments were carried out on the direct electrochemical synthesis reaction of sodium dichromate from sodium chromate. The kinetic data were experimentally measured at different temperatures and different initial sodium chromate concentrations of anolyte. The results show that the electrochemical synthesis process presents complicated zero-order reaction kinetic characteristics, with the reaction rate constant depending on the initial sodium chromate concentration. The macrokinetic equation of the electrochemical synthesis reaction was established, and some kinetic parameters were calculated. The apparent activation energy is less than that of the ordinary chemical reaction, and this shows that the electrochemical synthesis of sodium dichromate has great development potential.

Chromium-salt clean production process

Abstract: The invention discloses a kind of producing craft of chromic salt's cleanness. The invention adopts using waster to manage waster. Reclaim waste water of sodium acid sulfate and regard it as acidulant disposing chromium slag, acidify calcium chromate crystal which is in fusing chromium slag, aluminum residue and acid mud, and make it dissolve into fluid phase, reclaim its liquid to produce pigment of ceram or product of sodium dichromate. Select innoxious acid medicament at the same time, deoxidize hexavalent chromium into trivalent chromium under the acid condition and fix it in the chromium slag, and it discharges chromium slag and waste water innoxiously, simultaneously, dehydrate innoxious waste residue, dry it in the air or dry it in the oven, crush and pack it, we can sell it to cement mill to produce cement or use it as raw material in the production process of concrete, thus, it realises the purpose of cleanness of chromic salt.

Corrosion Inhibition of Aluminum Alloy in 50% Ethylene Glycol Solution

Abstract: The present study was conducted to evaluate the effect of different inhibitors on the corrosion rate of aluminum in 50% (v/v) ethylene glycol solution at 80°C and pH 8.0 in which the electrochemical technique of linear sweep voltammetry was employed to characterize each inhibitor function and to calculate the corrosion rate from Tafel plots generated by a computer assisted potentiostat. It is found that both sodium dichromate and borax reduces the corrosion rate by polarizing the anodic polarization curve while sodium phosphate, potassium phosphate, and sodium benzoate reduces the corrosion rate by polarizing both the anodic and cathodic polarization curve. When inhibitor concentration increases from I g/l up to 3 g/l, the inhibitor efficiency increases from 50% up to 85% for borax, from 64% up to 71% for sodium dichromate, and from 66% up to 82% for sodium phosphate, while constant inhibitor efficiency of about 55% and 50%for potassium phosphate and sodium benzoate were obtained respectively.

Method for producing dispersing agent using black water after producing nitrotoluenes, and the dispersing agent

Abstract: A method for preparing a dispersing agent is provided to produce a dispersing agent that has excellent dispersion and good stability and reduces phase separation by a consistency increase in a dispersion system. A method for preparing a dispersing agent includes a step of neutralizing waste generated from a preparation step of nitrotoluenes or oxidizing the waste after neutralization. The nitrotoluenes are mononitrotoluenes, dinitrotoluenes, or trinitrotoluenes. The neutralization is performed by using at least one neutralizer selected from the group consisting of sodium hydroxide, calcium hydroxide, potassium hydroxide, and sodium carbonate. The oxidation is performed by using at least one oxidant selected from the group consisting of a Fenton's reagent, hydrogen peroxide, potassium permanganate, potassium dichromate, ozone, sodium dichromate, and potassium persulfate.

Mild and Efficient Deprotection of the Amine Protecting p‐Methoxyphenyl (PMP) Group.

Abstract: Mild and efficient procedures for deprotection of the amine nitrogen protecting p-methoxyphenyl (PMP) group are described. Periodic acid and trichloroisocyanuric acid (TCCA) were found to be particularly effective in realizing amine liberation using 1 and 0.5 equiv of the oxidant, respectively. Extension of the periodic acid-mediated conditions to simultaneous alcohol oxidation by combination with a catalytic amount of sodium dichromate led to smooth conversion of PMP-protected Mannich products into the corresponding β-amino acids in a one-pot procedure.