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Breast milk chromium and its association with chromium intake, chromium excretion, and serum chromium.

Chromium metabolism of lactating women was evaluated by measuring diet, breast milk, urine, and serum chromium in 17 subjects 60 d postpartum. Breast milk chromium concentration was similar for the 3 d of collection with a mean +/- SE concentration of 3.54 +/- 0.40 nmol/L (0.18 ng/mL). Dietary intake and urinary chromium values were also similar for each of the 3 collection days. Total chromium intake of lactating mothers (0.79 +/- 0.08 mumol/d) was greater than that of reference female subjects (0.48 +/- 0.02). There was a significant correlation (r = 0.84) between serum chromium and urinary chromium excretion. If a breast milk volume of 715 mL is assumed, chromium intake of exclusively breast-fed infants is < 2% of the estimated safe and adequate daily intake of 10 micrograms. In summary, breast milk chromium content is independent of dietary chromium intake and serum or urinary chromium values. Chromium intake also did not correlate with serum or urine chromium but there was a significant relationship between serum and urinary chromium concentrations.

Adolescent↗

The binding of trivalent chromium to low-molecular-weight chromium-binding substance (LMWCr) and the transfer of chromium from transferrin and chromium picolinate to LMWCr.

A recent model for the role of chromium in insulin signaling requires that the oligopeptide low-molecular-weight chromium-binding substance (LMWCr) tightly bind four chromic ions before the oligopeptide obtains a conformation required for binding to the tyrosine kinase active site of the insulin receptor. To test this model, the chromium-binding constant of LMWCr was determined, and the ability of LMWCr to remove chromium from Cr2-transferrin and the nutritional supplement chromium picolinate, Cr(pic)3, was examined. These results are consistent with the model of the mode of action of LMWCr; a Hill study indicates the four chromic ions bind to apoLMWCr in a highly cooperative fashion (n =3.47) with a binding constant of 1.54x 10(21). Chromium is readily transferred from transferrin to apoLMWCr at near neutral pH. The results also suggest that reduction of the chromic center of Cr(pic)3 may be required for the supplement to release chromium; thus, release of chromium is related to a mechanism by which Cr(pic)3 may generate hydroxyl radicals in cells.

Carrier Proteins↗

Activation of chromium(VI) by thiols results in chromium(V) formation, chromium binding to DNA and altered DNA conformation.

The ability of the thiols glutathione, cysteine, beta-mercaptoethanol and dithiothreitol to effect chromium(VI)-induced DNA damage in vitro has been investigated. Reaction of pBR322 DNA with chromium(VI) in the presence of the thiols led to formation of chromium(V) and chromium--DNA adducts. The extent of chromium binding to DNA differed by several orders of magnitude among the thiols tested, in the order dithiothreitol greater than beta-mercaptoethanol much greater than cysteine greater than or equal to glutathione. The maximal level of chromium(V) formed also differed among the thiols tested, in the order beta-mercaptoethanol greater than dithiothreitol much greater than glutathione greater than or equal to cysteine. Electronic spectral studies of these reactions indicated that the rate of reduction of chromium(VI) is dependent on the thiol tested, in the order cysteine greater than dithiothreitol greater than glutathione greater than beta-mercaptoethanol. Electron paramagnetic resonance studies of these reactions indicate that a significant level of chromium(III) is detected only with cysteine. Chromium--DNA adducts formed by reaction of chromium(VI) in the presence of glutathione or cysteine did not lead to DNA conformational changes detectable upon agarose gel electrophoretic analysis. Changes in DNA conformation were detected as altered electrophoretic mobility of pBR322 DNA on agarose gels after reaction with chromium(VI) in the presence of dithiothreitol or beta-mercaptoethanol. Effects on DNA electrophoretic mobility, which depended on whether the initial conformation of the plasmid was linear or supercoiled, included altered and heterogeneous mobility, as well as complete inhibition of migration of the plasmid. Transmission electron microscopy of chromium--DNA complexes revealed aggregates of several plasmids, as well as condensation of individual plasmids into compact kinked forms. These effects may be due to cross-linking of DNA induced by chromium metabolites. These studies indicate that the levels of chromium bound to DNA are related to the levels and stabilities of the chromium(V) species formed upon reaction of chromium(VI) with the various thiols. Chromium--thiol interactions may play an important role in chromium(VI) genotoxicity.

Chromium↗

In vivo effects of ascorbate and glutathione on the uptake of chromium, formation of chromium(V), chromium-DNA binding and 8-hydroxy-2'-deoxyguanosine in liver and kidney of osteogenic disorder shionogi rats following treatment with chromium(VI).

Several previous in vitro studies have indicated that ascorbate and glutathione are the major reductants of Cr(VI) in cells. In order to evaluate the in vivo effects of ascorbate and glutathione on Cr(VI)-induced carcinogenesis, Cr uptake and the formation of Cr(V), Cr-DNA adducts and 8-hydroxy-2'-deoxyguanosine (8-OH-dG) were measured in the liver and kidney of Osteogenic Disorder Shionogi (ODS) rats that lack the ability to synthesize ascorbate. Despite a 10-fold difference in tissue ascorbate levels among different dietary ascorbate groups, the Cr(V) signal intensity, Cr uptake and total Cr-DNA binding were not affected in either organ. Treatment of ODS rats with Cr(VI) (10 mg/kg) had no substantial effect on the levels of ascorbate and glutathione in these tissues. The levels of Cr(V) and Cr-DNA binding were approximately 2-fold higher in the liver than in the kidney, although the levels of total Cr uptake were similar in both tissues. Cr uptake levels were significantly lower in the liver and kidney of ODS rats treated with high levels of ascorbate and a high dose of Cr(VI) (40 mg/kg), suggesting a detoxifying role played by plasma ascorbate. Similarly, modulation of glutathione levels by N-acetyl-L-cysteine, L-buthionine-S, R-sulfoximine or phorone in these animals by up to 2-fold had little or no consistent effect on Cr uptake, Cr-DNA binding, Cr(V) levels or 8-OH-dG formation in either organ. One possible explanation is that reduction of ascorbate and glutathione concentration to <10 and 50%, respectively, of normal in these two organs still provides threshold levels of these two reductants that are in excess of what is needed for significant reductive activation of Cr(VI). Alternatively, it is possible that ascorbate and glutathione do not play a major role in the formation of Cr(V), Cr-DNA binding or 8-OH-dG and that other cellular reductants, such as cysteine or other amino acids, might be more important reductants of Cr(VI) in vivo.

8-Hydroxy-2'-Deoxyguanosine↗

Supplemental-chromium effects on glucose, insulin, glucagon, and urinary chromium losses in subjects consuming controlled low-chromium diets.

The effects of low-chromium diets containing chromium in the lowest quartile of normal intake on glucose tolerance and related variables in 11 females and 6 male subjects were evaluated. Subjects with glucose concentration greater than 5.56 mmol/L but less than 11.1 mmol/L 90 min after an oral-glucose challenge were designated as the hyperglycemic group and the remainder, the control group. Glucose tolerance and circulating insulin and glucagon of the hyperglycemic group all improved during chromium supplementation (200 micrograms/d) whereas those of the control group were unchanged. Glucose and insulin concentrations 60 min after the oral-glucose challenge and the sum of the 0-90 min and 0-240 min glucose values were all significantly lower after chromium supplementation in the hyperglycemic group. These data demonstrate that consumption of diets in the lowest 25% of normal chromium intake lead to detrimental effects on glucose tolerance, insulin, and glucagon in subjects with mildly impaired glucose tolerance.

Adult↗

[Serum and erythrocyte chromium distribution and urinary elimination in persons occupationally exposed to chromium (VI) and chromium (III)].

With personal air samplers exposure to hexavalent and trivalent chromium was measured in 17 workers mainly exposed to Cr (VI) and in 7 workers mainly exposed to Cr (III) as basic chromium sulphate. Determination of Cr (VI) in urine of all the subject using a selective technique failed to show detectable amounts and postshift urinary total chromium was found, while urine levels of of workers exposed to chromic sulphate were not related to Cr. (III) air concentrations. Determination of total chromium in serum and red blood cells showed a significant increase of chromium levels in erythrocytes of workers exposed to Cr (VI) while in subjects mainly exposed to Cr (III) an increase of the serum fraction was evidenced. The results demonstrate that Cr (III) is absorbed through the respiratory tract but its kinetics and distribution in the body are different in comparison to Cr (VI) and not adequately monitored by short-term urinary determinations.

Animals↗

Reaction of chromium(VI) with ascorbate produces chromium(V), chromium(IV), and carbon-based radicals.

Reaction of potassium dichromate with sodium ascorbate was studied by EPR spectroscopy at room temperature, in 0.10 M N-[2-hydroxyethyl]piperazine-N'-[2-ethanesulfonic acid] (HEPES), phosphate, cacodylate, and tris(hydroxymethyl)aminomethane hydrochloride (Tris.HCl) buffers at pH 7.0, in the presence of 0.10 M spin trap [5,5-dimethyl-1-pyrroline 1-oxide or 2-methyl-N-(4-pyridinylmethylene)-2-propanamine N,N'-dioxide]. Chromium(V), ascorbate radical, CO2-, and other carbon-based spin trap-radical adducts were observed. Chromium(V), CO2-, and the carbon-based radicals were observed at low ratios of ascorbate to chromium, and ascorbate radical was observed at high ratios of ascorbate to chromium. The presence of Cr(IV) was detected indirectly by reaction with Mn(II) and a subsequent decrease in the Mn(II) EPR signal. More Cr(IV) was found for the higher reaction ratios of ascorbate to Cr(VI). The only buffer effect observed was a relative decrease of the Cr(V) signal in Tris.HCl vs HEPES, phosphate, and cacodylate buffers, no change in the radical adducts was observed. There was no evidence for reactive oxygen species an intermediates in this reaction. Addition of the singlet oxygen trap 2,2,6,6-tetramethyl-4-piperidone hydrochloride showed no 2,2,6,6-tetramethyl-1-piperidinyloxy radical formation. The Cr(V) species did not react with dioxygen, and dioxygen did not affect the formation of carbon-based radicals. A mechanism consistent with these observations is discussed.

Ascorbic Acid↗

Therapeutic review: is ascorbic acid of value in chromium poisoning and chromium dermatitis?

INTRODUCTION: Repeated topical exposure to chromium(VI) may cause an allergic contact dermatitis or the formation of chrome ulcers. Systemic toxicity may occur following the ingestion of a chromium(VI) salt, from chromium(VI)-induced skin burns, or from inhalation of chromium(VI) occurring occupationally. Soluble chromium(VI) salts are usually absorbed more easily and cross cell membranes more readily than trivalent chromium salts, and, therefore chromium(VI) is more toxic than chromium(III). In experimental studies, endogenous ascorbic acid in rat lung, liver, and kidney and human plasma, effectively reduces chromium(VI) to chromium(III). The administration of exogenous ascorbic acid has been advocated therefore in the treatment of systemic chromium poisoning and chromium dermatitis to enhance the extracellular reduction of chromium(VI) to the less bioavailable chromium(III). REVIEW: In vitro experiments confirm that the addition of ascorbic acid to plasma containing chromium(VI) leads to a dose-dependent reduction of chromium(VI) to chromium(III). In animal studies, parenteral ascorbic acid 0.5-5 g/kg significantly reduced chromium-induced nephrotoxicity when administered 30 minutes before parenteral sodium dichromate and up to 1 hour after parenteral sodium chromate dosing. Parenteral ascorbic acid 0.5-5 g/kg also reduced mortality when given orally up to 2 hours after oral potassium dichromate dosing. However, the administration of parenteral ascorbic acid more than 2 hours after parenteral chromate in these experimental studies did not protect against renal damage, and parenteral ascorbic acid given 3 hours postparenteral chromate increased toxicity. In addition, there is no confirmed clinical evidence that the administration of ascorbic acid lessens morbidity or mortality in systemic chromium poisoning. A possible reason for the lack of benefit of ascorbic acid when administration is delayed, is that chromium(VI) cellular uptake has occurred prior to ascorbic acid administration. Topical 10% ascorbic acid has been claimed to reduce significantly the healing time of experimentally induced chrome ulcers in guinea pigs. The proposed mechanism is reduction on the skin surface of chromium(VI) to chromium(III). Several case reports suggest that topical ascorbic acid is effective in the management of chromium dermatitis but this has not been confirmed in controlled clinical trials and, moreover, the practical difficulties of frequent application are likely to limit its usefulness. DISCUSSION: Based on experimental studies, substantial amounts of ascorbic acid would need to be administered, preferably parenterally, soon after exposure to prevent systemic toxicity from chromium(VI) in humans. However, as ascorbic acid is a metabolic precursor of oxalate, the administration of ascorbic acid in high dose could lead to acute oxalate nephropathy, particularly in the presence of renal failure. While smaller doses of ascorbic acid (e.g., 10 g intravenously) are not toxic, such doses probably will not reduce the mortality from systemic chromium poisoning. CONCLUSION: There is currently insufficient evidence to advocate the use of ascorbic acid in the management of systemic chromium toxicity. Topical ascorbic acid may reduce dermal hexavalent chromium exposure, but this observation must be confirmed in controlled studies.

Animals↗

Binding of chromium to chromatin and DNA from liver and kidney of rats treated with sodium dichromate and chromium(III) chloride in vivo.

The in vivo binding of chromium to whole chromatin, polynucleosomes, DNA, and cytoplasmic RNA-protein fraction from liver and kidney was examined after treatment of rats with sodium dichromate and chromium(III) chloride. Significant amounts of chromium were bound to DNA and the nonhistone proteins of chromatin and to cytoplasmic RNA-protein fraction. The binding of chromium to the nuclear and cytoplasmic nucleic acid fractions varied considerably, depending on the tissue and the oxidation state of the chromium administered. The level of chromium bound to whole chromatin was greater in the liver than in the kidney after treatment with either chromium compound. Chromium entered the liver and kidney tissues at a slower rate after chromium(III) treatment than after chromium(VI) treatment. At early times after chromium(VI) treatment, more chromium was bound to the liver and kidney chromatin and DNA than after chromium(III) treatment. A much smaller proportion of the chromium bound to chromatin was associated with the DNA after treatment with chromium(III) than after treatment with chromium(VI). However, 40 hr after injection, there was no significant difference in the level of chromium on the DNA from both the liver and kidney of chromium(VI)- and chromium(III)-treated animals. No DNA damage was detected in either liver or kidney nuclei after chromium(III) treatment, using the technique of alkaline elution. A possible correlation between chromium binding to chromatin and DNA damage is discussed.

Animals↗

Reduction of chromium(VI) to chromium(V) by rat liver cytosolic and microsomal fractions: is DT-diaphorase involved?

Incubation of rat liver cytosolic or microsomal fractions with chromium(VI) led to a dramatic decrease in chromium(VI) mutagenicity, as determined by the Ames Salmonella assay using the TA100 tester strain. The cytosol-dependent decrease in chromium(VI) mutagenicity was found to be counteracted in the presence of dicumarol, an inhibitor of the cytosolic enzyme NAD(P)H:quinone oxidoreductase (DT-diaphorase). In order to determine whether DT-diaphorase is a significant factor in enzymatic reduction of chromium(VI) in rat liver tissue, cytosolic and microsomal fractions were analyzed for NAD(P)H-dependent chromium (VI) reductase activity leading to chromium(V) formation by using electron paramagnetic resonance (EPR) spectroscopy. Reaction of chromium(VI) with NADH or NADPH in the presence of either cytosolic or microsomal fractions led to the formation of stable chromium(V)--NAD(P)H complexes. When glucose 6-phosphate (G6P) was present in the reaction as part of a NADPH-generating system, stable chromium(V)--G6P complexes were formed in addition to the chromium(V)--NAD(P)H complexes. The chromium(V) complexes had g values of 1.980-1.982 and superhyperfine splitting constants of 0.8-0.9 characteristic of bis(diol)oxochromium(V) complexes. Inhibition of 90% of the cytosolic DT-diaphorase activity by dicumarol led to only partial (20-22%) inhibition of chromium(V) formation. Visible and EPR spectroscopic studies showed that purified DT-diaphorase had no detectable chromium(VI) reductase activity and did not catalyze formation of chromium(V). Inhibition of 69% of microsomal aryl hydrocarbon hydroxylase activity by ketoconazole led to partial (10%) inhibition of chromium(V) formation. These results indicate that intracellular NAD(P)H-dependent enzymatic reduction of chromium(VI) in rat liver cannot be attributed to the activity of any one enzyme in the cytosolic or microsomal fractions. DT-diaphorase appears to play an indirect role in decreasing chromium(VI)-induced mutagenicity in Salmonella, possibly through interaction with other redox active cellular components. The involvement of diols such as sugars and pyridine nucleotides in stabilizing intracellularly generated chromium(V) is discussed.

Animals↗

Urinary chromium concentrations in humans following ingestion of safe doses of hexavalent and trivalent chromium: implications for biomonitoring.

In this study, we evaluate the significance of increased urinary chromium concentrations as a marker of chromium exposure and potential health risk. Six human volunteers ingested trivalent chromium [Cr(III)] and hexavalent chromium [Cr(VI)] at doses that are known to be safe but are much higher than typical dietary levels. The following dosing regimen was used: d 1-7, 200 micrograms/d chromium picolinate (a dietary supplement); d 8-10, Cr(VI) ingestion at the U.S. Environmental Protection Agency (EPA) reference dose (RfD) of 0.005 mg/kg/d; d 11-13, no dose; d 14-16, Cr(III) ingestion at the U.S. EPA RfD of 1.0 mg/ kg/d; and d 17-18, postdose. Urine voids were collected throughout the dosing periods and analyzed for chromium. Our findings are as follows: (1) ingestion of 200 micrograms/d of chromium picolinate yielded significantly elevated urine concentrations such that each participant routinely exceeded background, (2) ingestion of the Cr(VI) RfD (0.005 mg/kg/d) yielded individual mean urinary chromium levels (1.2-23 micrograms/L) and a pooled mean urinary chromium level (2.4 micrograms/L) that significantly exceeded background, and (3) ingestion of the Cr(III) RfD yielded no significant increase in urinary chromium concentrations, indicating that little, if any, absorption occurred. Our work identified three critical issues that need to be accounted for in any future studies that will use urinary chromium as a marker of exposure. First, a minimum urinary chromium concentration of approximately 2 micrograms/L should be used as a screening level to critically identify individuals who may have experienced elevated exposures to chromium. Second, if Cr(III) levels in soils are known to be less than 80,000 ppm and the Cr(III) is insoluble, urinary chromium concentrations are not an appropriate marker of exposure. Third, newer forms of chromium supplements that contain organic forms of Cr(III) must be considered potential confounders and their contribution to residential chromium uptake must be carefully evaluated.

Administration, Oral↗

Speciation of chromium in tanned leather gloves and relapse of chromium allergy from tanned leather samples.

There are concerns that wearing chromium tanned leather gloves can provoke a lapse of hand dermatitis in chromium sensitive patients. Various forms of chromium have different biological effects and the determination of total chromium (both soluble and insoluble), which often is used in clinical studies, may therefore not be an adequate measure of the adverse exposure. However, investigations, where dissolution of hexavalent chromium from leather gloves has been experimentally studied, could not been found in the literature. The aim of this pilot study was therefore to determine the total amount of chromium and the amount of sweat leachable chromium in different leather glove materials and also to apply samples of these materials in a patch test to chromium sensitive patients to see if they could provoke a reaction. The results showed tha chromium tanned leather contained about 3% (m/m) chromium. Chromium can also be found in dyed vegetable tanned leather, probably emanating from the leather dye. Small amounts (average 0.08% m/m) of leachable hexavalent chromium were found in both chromium and vegetable tanned leathers. Thus, the risk of relapse of chromium dermatitis cannot be disregarded and further studies on the causes of relapse of chromium dermatitis are necessary.

Chromium↗

Differential effects of chromium(VI) on constitutive and inducible gene expression in chick embryo liver in vivo and correlation with chromium(VI)-induced DNA damage.

The effect of DNA damage induced by the carcinogen chromium(VI) on the function of DNA as a template for transcription of constitutive and inducible genes was examined in chick embryo liver in vivo. Changes in gene expression, determined using solution hybridization and northern blot analyses to measure steady-state mRNA levels and a nuclear run-off assay to measure gene transcription rates, were compared to chromium-DNA binding and to chromium(VI)-induced DNA damage as previously measured by DNA alkaline elution. Chromium(VI) treatment had little or no effect on either the steady-state mRNA levels or the transcription rates of the constitutively expressed genes for albumin, conalbumin (avian transferrin), or beta-actin. In contrast, chromium(VI) treatment had significant but opposite effects on the basal and drug-inducible expression of 5-aminolevulinate synthase and cytochrome PB1 P450. The changes in steady-state expression of these two inducible genes were similar to the changes in transcription rate, indicating that the effects of chromium were principally transcriptional. Chromium(VI) treatment increased the basal expression of both inducible genes four- to fivefold at maximum, and the time course of this effect was similar to the time course for chromium(VI)-induced DNA damage and repair. In contrast, chromium(VI) pretreatment suppressed by 60-70% at maximum the subsequent induction of these genes by glutethimide, a phenobarbital analog, and the time course of this effect also corresponded to that of chromium(VI)-induced DNA damage and repair. The time courses of the changes in expression of these genes were bimodal, with the second peak corresponding closely to that of chromium(VI)-induced DNA cross-links. However, the first peak occurred during a period when no DNA cross-links or strand breaks were detectable by alkaline elution, although significant levels of chromium were bound to DNA. This suggests that chromium(VI), like cisplatin, may initially produce a DNA monoadduct that subsequently leads to DNA cross-link formation and that both types of chromium(VI)-induced lesions have a significant effect on the expression of targeted genes.

5-Aminolevulinate Synthetase↗

Fume generation and content of total chromium and hexavalent chromium in flux-cored arc welding.

This study was performed to investigate the fume generation rates (FGRs) and the concentrations of total chromium and hexavalent chromium when stainless steel was welded using flux-cored arc welding (FCAW) with CO2 gas. FGRs and concentrations of total chromium and hexavalent chromium were quantified using a method recommended by the American Welding Society, inductively coupled plasma-atomic emission spectroscopy (NIOSH Method 7300) and ion chromatography (modified NIOSH Method 7604), respectively. The amount of total fume generated was significantly related to the level of input power. The ranges of FGR were 189-344, 389-698 and 682-1157 mg/min at low, optimal and high input power, respectively. It was found that the FGRs increased with input power by an exponent of 1.19, and increased with current by an exponent of 1.75. The ranges of total chromium fume generation rate (FGRCr) were 3.83-8.27, 12.75-37.25 and 38.79-76.46 mg/min at low, optimal and high input power, respectively. The ranges of hexavalent chromium fume generation rate (FGRCr6+) were 0.46-2.89, 0.76-6.28 and 1.70-11.21 mg/min at low, optimal and high input power, respectively. Thus, hexavalent chromium, which is known to be a carcinogen, generated 1.9 (1.0-2.7) times and 3.7 (2.4-5.0) times as the input power increased from low to optimal and low to high, respectively. As a function of input power, the concentration of total chromium in the fume increased from 1.57-2.65 to 5.45-8.13% while the concentration of hexavalent chromium ranged from 0.15 to 1.08%. The soluble fraction of hexavalent chromium produced by FCAW was approximately 80-90% of total hexavalent chromium. The concentration of total chromium and the solubility of hexavalent chromium were similar to those reported from other studies of shielded metal arc welding fumes, and the concentration of hexavalent chromium was similar to that obtained for metal inert gas-welding fumes.

Air Pollutants, Occupational↗

Reaction of chromium(VI) with glutathione or with hydrogen peroxide: identification of reactive intermediates and their role in chromium(VI)-induced DNA damage.

The types of reactive intermediates generated upon reduction of chromium(VI) by glutathione or hydrogen peroxide and the resulting DNA damage have been determined. In vitro, reaction of chromium(VI) with glutathione led to formation of two chromium(V) complexes and the glutathione thiyl radical. When chromium(VI) was reacted with DNA in the presence of glutathione, chromium-DNA adducts were obtained, with no DNA strand breakage. The level of chromium-DNA adduct formation correlated with chromium(V) formation. Reaction of chromium(VI) with hydrogen peroxide led to formation of hydroxyl radical. No chromium(V) was detectable at 24 degrees C (297 K); however, low levels of the tetraperoxochromium(V) complex were detected at 77 K. Reaction of chromium(VI) with DNA in the presence of hydrogen peroxide produced significant DNA strand breakage and the 8-hydroxydeoxyguanosine adduct, whose formation correlated with hydroxyl radical production. No significant chromium-DNA adduct formation was detected. Thus, the nature of chromium(VI)-induced DNA damage appears to be dependent on the reactive intermediates, i.e. chromium(V) or hydroxyl radical, produced during the reduction of chromium(VI).

Animals↗

[Studies on a specific chromium binding substance (a low-molecular-weight chromium binding substance) in urine (author's transl)].

The aim of this study was to identify a specific substance [a Low-Molecular-Weight Chromium binding substance (LMW Cr)] in normal urine and also to clarify the various factors affecting chromium to bind this substance in urine. The results obtained were as follows: 1. Normal human and rat urines contained unsaturated LMW Cr similar to that found in the liver or other organs of rabbits and dogs. The amount of chromium bound in vitro to the unsaturated LMW Cr in normal human urine was 14.81 +/- 1.84 microgram/ml urine when urine was incubated with trivalent chromium for 30 minutes at 37 degrees C. 2. Higher amounts of chromium were bound to LMW Cr in normal urine a 37 degrees C than at 24 degrees C, in acidic state of urine than in alkaline state, and when trivalent chromium was added to the incubation mixture than when hexavalent chromium was added. Chromium contained in LMW Cr was supposed to be trivalent. Furthermore, boiling urine at 100 degrees C for 10 minutes did not reduce the chromium binding capacity of LMW Cr in urine. These results indicate that LMW Cr in urine binds chromium by a chemical reaction. 3. Amounts of chromium bound to LMW Cr in urine obtained 3 hrs after intraperitoneal injection of 200 mumole K2Cr2O7 to a rat were much higher than amounts of chromium bound in vitro to LMW Cr in normal urine during 3 hrs incubation of the urine with K2Cr2O7. This suggests that most of excessively absorbed chromium is excreted into urine after being bound to LMW Cr in organs. 4. Urine from patients with chronic nephritis excreted a part of added chromium bound to high molecular weight fractions corresponding to peaks of UV absorption.

Adult↗

Quantification of total chromium and hexavalent chromium in UHT milk by ETAAS.

Procedures for the quantification of total chromium and hexavalent chromium in UHT milk samples are presented. Total chromium was determined directly in milk with the addition of a surfactant and a mixture of Pd and Mg as a chemical modifier. For the selective separation of hexavalent chromium, the sample pre-treatment consisted in precipitation of proteins and elution of the supernatant through a Chromabond NH2 column. The metal was eluted with nitric acid. Both total chromium and hexavalent chromium were evaluated by atomic absorption spectrometry with electrothermal atomization using the same instrumental conditions. The detection limits were 0.2 and 0.15 microgram l-1 for total chromium and hexavalent chromium, respectively. The linearity ranges under the optimized conditions were 0.2-20 and 0.15-50 micrograms l-1. For total chromium the precision was 4.9 and 5.7% for the analytical and the over-all procedure, respectively, and for hexavalent chromium 4.3 and 4.9%, respectively. The validation of both procedures was performed by the standard additions method and the recoveries were higher than 93% in all cases. For total chromium, a certified reference material was also used to validate the methodology. The methods were applied to the determination of total chromium and hexavalent chromium in 60 UHT milk samples.

Animals↗