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Mammalian cell transformation induced by chromium(VI) compounds in the presence of nitrilotriacetic acid.

We used a soft agar assay on cultured Syrian hamster fibroblasts to determine the ability of nitrilotriacetic acid (NTA) and Cr(VI) compounds to induce malignant cell transformation. Induction of extended anchorage-independent growth was detected in BHK 21/c13 cells by scoring colonies of transformed cells visible to the naked eye 20-25 d after plating in growth medium containing agar. Survival was determined by plating cells in liquid medium without agar and by counting the number of macroscopic colonies after 7-10 d. Mitomycin C and 4-nitroquinoline 1-oxide were used as reference direct transforming agents, with clearly positive results. In our hands no increase of the spontaneous transformation rate of BHK cells was induced by NTA concentrations ranging from 2 X 10(-3) to 10(-2) M, although the survival index was significantly reduced above 4 X 10(-3) M NTA. Two Cr(VI) compounds, K2Cr2O7, which is highly soluble in water, and CaCrO4, which is partially soluble, were tested in the soft agar assay either in the absence or in the presence of NTA. When used alone, both compounds behaved as positive transforming agents. NTA increased 4 or 10 times the cytotoxicity and the transforming activity of CaCrO4 and K2Cr2O7, respectively. As the amounts of soluble Cr(VI) detectable in the K2Cr2O7 and CaCrO4 solutions were not increased in the presence of NTA, a synergistic interaction between NTA and soluble Cr(VI) is inferred.

Acetates↗

One hundred years of chromium and cancer: a review of epidemiological evidence and selected case reports.

The present review is motivated by the fact that 100 years have passed since the first cancer case in a chromium worker was reported in Scotland. Old and recent case reports and epidemiological studies among chromate workers are reviewed to elucidate the importance of valency states and water solubility of chromium compounds for carcinogenic potency. It is concluded that all chromium[VI] compounds should be considered carcinogenic among exposed populations, and that no evidence has been presented indicating that human exposure to chromium[III] is associated with increased cancer risk. Strong evidence has been presented that zinc chromate is a potent carcinogen and suggests that calcium chromate may be a potent carcinogen. Evidence also suggests that water-soluble chromates in general may be more potent carcinogens than those with low solubility. Primary and secondary prevention of chromate-related cancer and the success in preventive measures are briefly discussed, and recommendations for future research are made.

Chromates↗

Threshold mechanisms and site specificity in chromium(VI) carcinogenesis.

Ten years have elapsed since the International Agency for Research on Cancer (IARC) evaluated the carcinogenicity of chromium and chromium compounds. Further studies performed during the last decade have provided further epidemiological, experimental and mechanistic data which support the IARC conclusions. A wealth of results indicate that, at variance with chromium(0) and chromium(III), chromium(VI) can induce a variety of genetic and related effects in vitro. The lack of carcinogenicity of chromium(0) and chromium(III) compounds in experimental animals is well established, and only a minority of animal carcinogenicity data with chromium(VI) compounds were positive (30 out of 70, i.e. 42.9%). Moreover, most positive studies used administration routes which do not mimic any human exposure and by-pass physiological defense mechanisms. Typically, positive results were only obtained at implantation sites and at the highest dose tested. Exposure to chromium(VI) has been known for more than a century to be associated with induction of cancer in humans. Carcinogenicity requires massive exposures, as is only encountered in well defined occupational settings, and is site specific, being specifically targeted to the lung and, in some cases, to the sinonasal cavity. Increased death rates for cancers at other sites, which were occasionally reported in some epidemiological studies, were almost invariably not statistically significant, and inconsistent (being counterbalanced by other studies which apparently showed decreased rates for the same cancers). As we recently quantified in human body compartments, chromium(VI) can be reduced in body fluids and non-target cells, which results in its detoxification, due to the poor ability of chromium(III) to cross cell membranes. In target cells, chromium(VI) tends to be metabolized by a network of mechanisms leading to generation of reduced chromium species and reactive oxygen species, which will result either in activation or in detoxification depending on the site of the intracellular reduction and its proximity to DNA. When introduced by the oral route, chromium(VI) is efficiently detoxified upon reduction by saliva and gastric juice, and sequestration by intestinal bacteria. If some chromium(VI) is absorbed by the intestine, it is massively reduced in the blood of the portal system and then in the liver. These mechanisms explain the lack of genotoxicity, carcinogenicity, and induction of other long-term health effects of chromium (VI) by the oral route. Within the respiratory tract, chromium(VI) is reduced in the epithelial-lining fluid, pulmonary alveolar macrophages, bronchial tree and peripheral lung parenchyma cells. Hence, lung cancer can only be induced when chromium(VI) doses overwhelm these defense mechanisms. The efficient uptake and reduction of chromium(VI) in red blood cells explains its lack of carcinogenicity at a distance from the portal of entry into the body. All experimental and epidemiological data, and the underlying mechanisms, point to the occurrence of thresholds in chromium(VI) carcinogenesis.

Administration, Inhalation↗

[Nephrotoxic action of platinum, chromium and cadmium compounds on marine bony fishes].

Intra-abdominal injections of platinum, chromium and cadmium salts to Myoxocephalus scorpius produce nephrotoxic effect which includes the disturbances in magnesium secretion. Basic ultrastructural changes in the nephron cells of the fish after the injection of nephrotoxic substances are similar to those in mammals. Cis-platinum induces significant damage in the terminal part of the proximal tubules. One day after the injection of chromium compounds, total damage of the proximal tubule is observed, whereas cadmium salt affects cells within the whole nephron. After 5 days of administration of cadmium and chromium salts, partial recovery was found with respect to both functional and ultrastructural properties of nephron cells. Administration of nephrotoxic substances which selectively injure different parts of the nephron enabled to perform more exact differentiation of the nephron elements in marine teleosts.

Animals↗

Comparative studies of chromosomal aberration and mutagenicity of the trivalent and hexavalent chromium.

The comparative cytogenetic and mutagenic effects between trivalent and hexavalent chromium were investigated. Five chromium compounds, K2Cr2O7 and K2CrO4 containing Cr6+, and Cr(CH3COO)3, Cr(NO3)3 and CrCl3 containing Cr3+, were examined for their ability to induce chromosomal damage in cultures of human leukocytes, for their reactivity with DNA by a rec-assay system and for mutagenicity in the E. coli Hs30R test system. Chromosome-breaking activity was significantly higher for the compounds with hexavalent than trivalent chromium, the efficiency being in the decreasing order K2Cr2OM greater than K2CrO4 greater than Cr(CHCOO)3 greater than Cr(NO3)3, CrCl3. In the rec-assay and mutation assay, hexavalent (K2Cr2O7 and K2CrO4) and trivalent Cr(CH3COO)3) compounds gave positive results, their mutagenic potential being higher in the same order of clastogenic magnitude.

Cells, Cultured↗

Absorption of inorganic, trivalent and hexavalent chromium following oral and intrajejunal doses in rats.

The intestinal absorption of trivalent and hexavalent chromium (Cr) given orally (experiment I) or infused in the intestine (experiment II) was investigated in rats. The nonabsorbable form of chromium (51Cr2O3) and water-soluble and more absorbable Na2(51)CrO4 (the hexavalent form of Cr) were compared. Total retention of chromium given orally ranged around 15 percent of the dose, regardless of the chromium compounds applied. The absorption rate of chromic oxide, which is considered a nonabsorbable compound, was 14.4 as a percentage of chromium intake. This result indicates that some loss of chromium has to be taken into account in metabolic trials made by the indicator method. In isolated rat intestine, from the injected Cr 2.5% of chromic oxide and 43.2% of sodium chromate were absorbed during an hour (experiment II). The absorbed chromium was transferred to the liver where the liver tissue retained 10.9% of chromic oxide and 51.1% of sodium chromate. Radioactivity of v. cava caudalis following intestinal injection of Na2CrO4 was thirtyfold greater than after Cr2O3 dosing. This phenomenon can be explained by the lower blood clearance of chromate. Different absorption rate of chromate depending on the route of administration could be due to the fact that the hexavalent form given orally was reduced to Cr3+ in the acidic environment of the stomach. When Na2CrO4 was infused directly in the intestine of rats, such reduction could not occur. This means that the acidic gastric juice might play a role in inhibiting the intestinal absorption of Na2CrO4 when this compound is given orally.

Administration, Oral↗

Induction of SOS response in Escherichia coli strain PQ37 by 16 chemical compounds and human urine extracts.

The SOS Chromotest on Escherichia coli strain PQ37 was used to detect DNA damage induced by 16 chemical compounds and urine samples from smokers and a non-smoking psoriatic patient treated with mineral coal tar. The results confirmed the strong SOS inducing activity of 2-aminoanthracene and benzo[a]pyrene with metabolic activation and N-methyl-N'-nitro-N-nitrosoguanidine, mitomycin C and 4-nitroquinoline-N-oxide without metabolic activation. A weaker response in the absence of microsomal enzymes was observed with hydroxyurea (only at high doses) and the soluble Cr(VI) compounds potassium chromate and potassium dichromate. No effect was observed with ampicillin, cadmium chloride, cyclophosphamide, griseofulvin, the insoluble Cr(VI) compound lead chromate, the soluble Cr(III) compounds chromium nitrate, chromium chloride, chromium potassium sulphate, and the chelating agent sodium nitrilotriacetate. Among the Cr(III) compounds only chromium acetate produced a low but significant increase of SOS inducing activity. Solubilization by nitrilotriacetate of genotoxic Cr(VI) from insoluble lead chromate was observed, whereas no interaction occurred between nitrilotriacetate and the soluble Cr(VI) and Cr(III) compounds. Using urinary XAD-2 extracts, we found the SOS Chromotest poorly sensitive to the mutagens present in urine from tobacco smokers which, on the other hand, were detected by the gene mutation assay in Salmonella typhimurium (Ames test). A urine sample obtained from a psoriatic patient, therapeutically treated with mineral coal tar, had a significant SOS inducing activity with and even without metabolic activation, whereas in the Ames test it was active only in the presence of metabolic activation.(ABSTRACT TRUNCATED AT 250 WORDS)

Alkaline Phosphatase↗

The health hazards posed by chromium-contaminated soils in residential and industrial areas: conclusions of an expert panel.

Between 1905 and 1971, over 2 million tons of residue from chromite ore processing was generated in Hudson County, New Jersey, of which substantial amounts were used as fill and tank diking. A panel of medical, toxicology, and risk assessment experts was convened in early 1990 to evaluate the potential health hazards posed by the resulting chromium contaminated soil. The Panel concluded that soils containing concentrations of 75 ppm hexavalent chromium [Cr(VI)] and 1000 ppm total chromium compounds (about 95% was trivalent chromium [Cr(III)]) did not pose a significant health hazard to nearby residents and workers. They also determined that exposure to chromium from Hudson County sites posed a negligible cancer hazard to residents. Using risk assessment methods, the Panel estimated that the plausible incremental cancer risk to individuals at residential sites would be substantially less than 1 in 1,000,000. The average measured levels of airborne Cr(VI) at typical industrial sites were more than 1000-fold lower than the current OSHA Permissible Exposure Limit (PEL). The maximum plausible increased cancer risk for an average worker at a dusty industrial site was estimated to be less than 1 in 100,000. The Panel also concluded that chromium-containing crystals, which have occasionally been found in Hudson County buildings, do not pose a significant hazard. However, they suggested that were the concentration to exceed 5000 ppm Cr(VI) in the crystals, site-specific health risk assessments would be conducted and remediation considered. The Panel evaluated the dermal hazard posed by chromium-contaminated soil and acknowledged that there is a small group of persons (approximately 0.1% of the United States population) who currently have a dermal sensitization to Cr(VI) primarily through occupational exposure. Based on published studies of human volunteers, the Panel concluded that a small percentage (less than 5%) of persons already sensitized may respond to Cr(VI) in solution at concentrations above 35 ppm. They decided that a much higher concentration in soil, perhaps 350 ppm Cr(VI), would be necessary to elicit dermatitis because only a fraction of the chromium in soil is soluble. The Panel concluded that it was highly unlikely (if not impossible) for a person to become dermally sensitized to Cr(VI) or Cr(III) at the soil concentrations found in most areas in Hudson County.(ABSTRACT TRUNCATED AT 400 WORDS)

Air Pollutants↗

The analytical biochemistry of chromium.

The essentiality and carcinogenicity of chromium depend on its chemical form. Oxidation state and solubility are particularly important in determining the biological effects of chromium compounds. For this reason, total chromium measurements are of little value in assessing its nutritional benefits or its toxicological hazards. Aqueous sodium carbonate-sodium hydroxide solutions have been successfully used for extracting hexavalent chromium from a variety of environmental and biological matrices while preserving its oxidation state. Typical recoveries are 90 to 105% in samples spiked with both trivalent and hexavalent chromium. Determination of hexavalent chromium after extraction with sodium carbonate-sodium hydroxide solution, coupled with the determination of total chromium after nitric acid-hydrogen peroxide digestion, has been applied to the evaluation of chromium speciation in airborne particulates, sludges, and biological tissues.

Carcinogens, Environmental↗

Oral bioavailability of chromium from a specific site.

Analysis of soil from a specific site in New Jersey indicated a low level of sodium and chromium present as a calcium compound. Chromium was then administered orally to young, mature male rats at a level of 240 micrograms/kg for 14 days as chromium-contaminated soil, as CaCrO4, and as an equimolar mixture of the soil and calcium salts for 14 days. The rats were sacrificed 24 hr after the last dosing, and tissues were taken immediately for chromium analysis. Blood, muscle, and liver contained the highest levels of chromium in these animals, although kidney contained the highest concentration per gram of tissue. The total amount of chromium in the tissues was less than 2% of the administered chromium. In a study of the excretion of chromium, the animals were dosed orally for 8 days (with CaCrO4 or contaminated soil, each at the level of 240 mumole Cr/kg), and the chromium in feces and urine was determined on days 1, 2, 7, and 8. After cessation of dosing for 27 days, the same rats were dosed for 2 days at the same level, and chromium in urine and feces was determined for the 2 days. The animals administered the chromium in soil had higher levels of chromium in both urine and feces on all days compared to the group fed the CaCrO4. The total recovery of chromium in any of the 2-day periods was less than 50% of the chromium administered during that period.

Administration, Oral↗

Absence of tubular proteinuria following environmental exposure to chromium.

Certain chromium compounds are known to be nephrotoxic, but renal damage from long-term environmental or occupational exposure to chromium has not been documented. To detect possible preclinical renal damage, we tested the urine of 55 lifelong residents of an area contaminated with chromium landfill. The levels of four proteins were determined in urine samples: (1) human intestinal alkaline phosphatase, (2) tissue nonspecific alkaline phosphatase, (3) N-acetyl-beta-D-glucosaminidase, and (4) microalbumin. No elevated levels of proteins were found, and there were no significant correlations between urine protein and urine chromium concentrations. We concluded that long-term environmental exposure to chromium dust did not lead to tubular proteinuria.

Adult↗

Mutagenicity and toxicity of chromyl chloride and its vapours.

Chromyl chloride (CC), a liquid Cr6+ compound suspected of carcinogenic activity, was assayed for mutagenicity in the Ames reversion test. Due to its high volatility and toxic and corrosive properties, handling of CC required particular precautions. The liquid phase of CC elicited dose-related mutations in Salmonella typhimurium, strain TA100, although it had a limited range of activity because of its toxicity to the bacteria. The mutagenic potency and the toxic activity were of the same order of magnitude as all the water-soluble Cr6+ compounds so far tested. Toxic and mutagenic activities could also be clearly detected by using a variety of modifications of the Ames test in CC vapours which indicates the particular danger of this chromium compound. In analogy with the other Cr6+ compounds previously tested in this laboratory, all the effects observed were decreased in the presence of S-9 mix containing rat liver post-mitochondrial fractions.

Chlorides↗

[Experiment study on the estrogen-like effect of compounds of mercury, chromium and manganese].

OBJECTIVE: In order to study estrogen-like effect of compounds of Mercury, Chromium and Manganese. METHODS: Mercury Chloride, Manganese Sulfate, Chromium Chloride and Chromium trioxide were selected to perform proliferation assay of MCF-7 human breast cancer cells and binding assay of estrogen receptor for rat uterine. RESULTS: Mercury Chloride could stimulate the proliferation of MCF-7 cell, the maximal increase of MCF-7 cells was measured by Mercury Chloride at 10(-7) mol/L. The effect was blocked completely by a pure antigestrogen ICI182, 780; but Mercury Chloride could not bind to ER by competing with E2. Chromium Chloride, Chromium Trioxide and Manganese Sulfate were not able to stimulate the proliferation of MCF-7 cell and bind to ER through competing against 3H-E2 in vitro. CONCLUSION: Mercury Chloride exhibited the estrogenicity through binding and activating ER; Chromium Chloride, Chromium trioxide and Manganese Sulfate did not show any estrogenicity.

Animals↗

Micronucleus induction by chromium and selenium, and suppression by metallothionein inducer.

The clastogenic effects of chromium compounds (CrCl3 and K2CrO4) and selenium compounds (H2SeO3 and Na2SeO4) in mouse bone marrow cells have been investigated. K2CrO4 induced significant, dose-related increases in micronuclei. H2SeO3 also showed a significant micronucleus induction at the highest dose. CrCl3 and Na2SeO4 were negative for micronuclei induction in mice. The suppressive effect of Bi(NO3)3, a metallothionein inducer, on the micronucleus induction by K2CrO4 and H2SeO3 has been also investigated. Pretreatment with Bi(NO3)3 suppressed the micronucleus induction by K2CrO4 and H2SeO3. In addition, the incidence of micronucleus induction seemed to be reduced by double dosing with K2CrO4 and H2SeO3, compared to single dosing. It is generally recognized that a number of metal compounds induce metallothionein synthesis. These results suggest that the mechanism of suppression of micronucleus induction by K2CrO4 and H2SeO3 involve possible participation of metallothionein in mouse bone marrow.

Animals↗