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Induction of oxidative stress by chronic administration of sodium dichromate [chromium VI] and cadmium chloride [cadmium II] to rats.

Recent studies have demonstrated that both chromium (VI) and cadmium (II) induce an oxidative stress, as determined by increased hepatic lipid peroxidation, hepatic glutathione depletion, hepatic nuclear DNA damage, and excretion of urinary lipid metabolites. However, whether chronic exposure to low levels of Cr(VI) and Cd(II) will produce an oxidative stress is not shown. The effects of oral, low (0.05 LD50) doses of sodium dichromate [Cr(VI); 2.5 mg/kg/d] and cadmium chloride [Cd(II); 4.4 mg/kg/d] in water on hepatic and brain mitochondrial and microsomal lipid peroxidation, excretion of urinary lipid metabolites including malondialdehyde, formaldehyde, acetaldehyde and acetone, and hepatic nuclear DNA-single strand breaks (SSB) were examined in female Sprague-Dawley rats over a period of 120 d. The animals were treated daily using an intragastric feeding needle. Maximum increases in hepatic and brain lipid peroxidation were observed between 60 and 75 d of treatment with both cations. Following Cr(VI) administration for 75 d, maximum increases in the urinary excretion of malondialdehyde, formaldehyde, acetaldehyde, and acetone were 2.1-, 1.8-, 2.1-, and 2.1-fold, respectively, while under the same conditions involving Cd(II) administration approximately 1.8-, 1.5-, 1.9-, and 1.5-fold increases were observed, respectively, as compared to control values. Following administration of Cr(VI) and Cd(II) for 75 d, approximately 2.4- and 3.8-fold increases in hepatic nuclear DNA-SSB were observed, respectively, while approximately 1.3- and 2.0-fold increases in brain nuclear DNA-SSB were observed, respectively. The results clearly indicate that low dose chronic administration of sodium dichromate and cadmium chloride induces an oxidative stress resulting in tissue damaging effects that may contribute to the toxicity and carcinogenicity of these two cations.

Acetaldehyde↗

A comparative study of the effects of inhaled cadmium chloride and cadmium oxide: pulmonary response.

The effects of aerosols of cadmium chloride (CdCl2) and cadmium oxide (CdO) on pulmonary biochemical function were compared. Rats and rabbits were exposed to 0.25, 0.45, or 4.5 mg Cd/m3 for 2 h. Pulmonary toxicity was determined histologically and biochemically. Cadmium chloride and CdO showed a deposition response that was linearly related to the chamber concentration. Both compounds caused multifocal, interstitial pneumonitis 72 h after exposure, but the CdO lesion was more severe with proliferation of fibrocytic-like cells as well as pneumocytes. Comparing the two Cd compounds at the highest concentration (4.5 mg Cd/m3), the biochemical responses in the rat were similar. The majority of the effects occurred 72 h after exposure, with significant increases in lung weight, lung-to-body weight ratio, GSH reductase, GSH transferase, and G-6-PDH. However, GSH peroxidase was inhibited immediately after the CdO exposure. Cadmium oxide-related alterations in the parameters studied could easily be distinguished from those of CdCl2 at the exposure concentration of 0.45 mg Cd/m3. The response pattern in the rabbit resembled that of the rat. In both species Cd had a consistent inhibitory effect on pulmonary GSH peroxidase, even at the lowest concentration of 0.25 mg Cd/m3. Based on these findings, inhaled CdO appeared to be more toxic to the lung than inhaled CdCl2.

Aerosols↗

Studies on the dominant-lethal and fertility effects of the heavy metal compounds methylmercuric hydroxide, mercuric chloride, and cadmium chloride in male and female mice.

Dominant-lethal effects of 10 mg/kg methylmercuric hydroxide were studied in male mice from two hybrid stocks and in females from one of these stocks. Two other compounds, mercuric chloride (2 mg/kg) and cadmium chloride (2 mg/kh), were studied only in females for dominant-lethal (in one hybrid stock) and reproductive capacity effects (in two hybrid and one mixed stocks). All compounds were administered in a single intraperitoneal injection. When males of one of the two stocks studied were treated with methylmercuric hydroxide, the females to which they were mated exhibited a slight reduction in the total number of implantations and in the number of living embryos. These reductions were accompanied by a very small increase in the incidence of dead implantations. In females, cadmium chloride had no detectable dominant-lethal or other fertility effects, except superovulation. On the other hand, the two mercury compounds slightly reduced the numbers of implants and living embryos in females subjected to dominant-lethal studies. The two mercury compounds also induced a slight reduction in that long-term reproductive performance of one stock of females. These results and those reported earlier by others, indicate that the mercury compounds studied so far are not potent inducers of dominant-lethal mutations in male and female mice. It is not clear whether the small effects on male or female fertility induced in some cases, particularly the increase in dead implantations and reductions in the number of living embryos, were attributable to dominant-lethal mutations or to nongenetic causes.

Animals↗

Lung deposition, lung clearance and renal accumulation of inhaled cadmium chloride and cadmium sulphide in rats.

Rats were exposed 6 h/day over 10 days to 0.3 mg/m3 of water soluble cadmium chloride and 0.2, 1.0 and 8.0 mg/m3 of insoluble cadmium sulphide, then killed at intervals over a 3-month period for serial measurements of lung, renal and faecal cadmium. CdCl2 and high-dose CdS animals showed a transient increase in lung weight. Clearance of both compounds was biphasic. Approximately 40% of deposited material was cleared during the 10-day exposure period. For CdCl2, only 9% of the lung burden was cleared rapidly after the last exposure (half-life 1.0 days) and 47% slowly (half-life 87 days), leaving a residual lung burden of 44%. For CdS, 41% of the lung burden was cleared rapidly (half-life 1.4 days) and 40% slowly (half-life 42 days), leaving a final residue 19%. In the CdS high-dose group, the retention of CdS in the lung was greater than that in the CdS low-dose groups, indicating that clearance mechanisms may possibly have been impaired in the high-dose group by too great a lung burden. For both compounds, faecal cadmium was initially high. Renal accumulation of cadmium was substantial for CdCl2 during the exposure period and continued over the following months until it represented approximately 35% of the total cadmium cleared from the lung. For CdS, renal accumulation was only 1% of the amount cleared from the lung. The bioavailability of Cd from CdS is thus poor, the majority being cleared from the lungs and excreted in the faeces. However, the bioavailability of inhaled CdS measured as cadmium in the kidney is greater than the bioavailability of orally ingested CdS.

Administration, Inhalation↗

Effect of mercuric chloride and cadmium chloride on gonadal function and its regulation in sexually mature common carp Cyprinus carpio.

Gonadal function in fish, Cyprinus carpio was significantly affected by sublethal doses of mercuric chloride (HgCl2) and cadmium chloride (CdCl2) in chronic (45 days) exposure. Parameters investigated were nonesterified (NE) and esterified (E) cholesterol of ovary, liver and serum and ovarian 3 beta-Hydroxysteroid and 17 beta-Hydroxysteroid dehydrogenase enzyme activity and serum and pituitary gonadotropin (GtH) levels. Both the pollutants were able to reduce the hypothalamic extract (HE) or gonadotropin releasing hormone (GnRH) induced pituitary GtH release in vitro. Short term (96h) exposure of the fish to the pollutants had no significant effect on the gonadal function. In addition to the deleterious effect of pollutants on the gonadal steroidogenesis and pituitary gonadotropin release, using [4-14C] cholesterol as a tracer it was found that for 45 days exposure, HgCl2 had an adverse effect on the transport of cholesterol from circulation to ovary.

Animals↗

Cadmium chloride and cadmium metallothionein-induced pulmonary injury and recruitment of polymorphonuclear leukocytes.

Pulmonary exposure of rats to either cadmium chloride (CdCl2) or cadmium metallothionein (CdMT) was previously reported to induce an influx of polymorphonuclear leukocytes (PMNs) to the airways, but only CdCl2 caused a significant increase in lung permeability, indicative of damage to the pulmonary epithelium. The purpose of this study was to investigate mechanisms of PMN recruitment following exposure to these forms of cadmium. Fischer 344 rats were intratracheally instilled with 10 micrograms cadmium in the form of CdCl2 or CdMT, and the time course of pulmonary inflammation and PMN migration activity was determined. PMN numbers, permeability, and PMN migration activity of lung lavage supernatant peaked 1 to 2 days after CdCl2 exposure. PMN migration activity was not detected 5 h after CdMT exposure, despite a peak of PMN numbers 10 h after exposure, but was increased by 1 day when permeability had increased to a small but significant degree. Elastase-modified forms of alpha-1-proteinase inhibitor (alpha 1PI), with molecular weights of 80 and 51 kd, have been reported to be highly chemotactic for PMNs. Antiserum to alpha 1PI significantly inhibited PMN migration activity detected in supernatants 1 day after exposure to either CdCl2 or CdMT. The results suggest that both CdCl2 and CdMT induce the formation of high molecular weight modified forms of alpha 1PI in the airways; these factors may traverse damaged epithelium to recruit PMNs from the vasculature. Additional small or lipophilic factors, undetectable by the methods of this study, may be responsible for the early influx of PMNs following CdMT exposure in the absence of increased epithelial permeability.

Adult↗

Toxicities of combinations of pentachloronitrobenzene with mercuric chloride or cadmium chloride, and hexachlorobenzene with mercuric chloride administered to rats.

1. Pentachloronitrobenzene (PCNB) and HgCl2, PCNB and CdCl2, and hexachlorobenzene (HCB) and HgCl2 were investigated for their acute oral toxicity in rats, individually and as combinations in various ratios of the organochlorine pesticides to the heavy metal chlorides. 2. The toxicity of mixtures of low dosages of the pairs tested was higher than the sum of the toxicities produced by the individual doses. 3. At increased dosages of the components in the combinations PCNB-HgCl2 and PCNB-CdCl2, the combined lethality tended towards the sums of the effects of the individual doses.

Animals↗

Single crystal EPR studies on Mn(II)-doped sarcosine cadmium chloride and sarcosine cadmium bromide: study of zero-field splitting tensor in iso-structural complexes.

EPR spectra of single crystals of Mn(II)-doped sarcosine cadmium chloride and sarcosine cadmium bromide are studied in Q-band and in X-band at room temperature. Two magnetically inequivalent sites are observed in both the lattices in a distorted octahedral environment. The spin-Hamiltonian parameters are extracted and are found to have a rhombic symmetry. The angular variation of the zero-field transitions is simulated for one of the sites with an asymmetric zero-field tensor D = 480 x 10(-4) cm(-1), E = -115 x 10(-4) cm(-1) and a = 10 x 10(-4) cm(-1) for Mn(II) in sarcosine cadmium chloride and with D = 460 x 10(-4) cm(-1) E = -98 x 10(-4) cm(-1) and a = 10 x 10(-4) cm(-1) for Mn(II) in sarcosine cadmium bromide. The observed large value of zero-field tensor is due to the steric effects of the crystal packing caused by the ligands. Matumura's plot predicts an average covalency of 8.8 and 7.7% for the manganese-ligand bond in SCC and SCB lattices respectively.

Bromides↗

Response of rat hepatocyte cultures to cadmium chloride and cadmium-diethyldithiocarbamate.

Cellular effects of cadmium (Cd) were studied in primary cultures of rat hepatocytes incubated with cadmium chloride (CdCl2) or cadmium-diethyldithiocarbamate (Cd(DTC)2), labelled with 109Cd. The lipid-soluble complex Cd(DTC)2 was rapidly taken up into the cells and a maximal concentration was reached after 4 h incubation. On the other hand, incubation with CdCl2 resulted in a slow, continuous accumulation of Cd for up to 20 h. Cd was found to be associated with proteins to a higher extent when added to the incubation medium as CdCl2 than when added as Cd(DTC)2, which in addition to differences in lipophilicity of the Cd compounds partly explains the differences in Cd uptake. Subcellular distribution studies showed that a significantly higher proportion of Cd was associated with the total particulates fraction in cells after incubation with Cd(DTC)2 compared to CdCl2 (32 and 19%, respectively). The activities of glutathione reductase and succinic dehydrogenase were inhibited to a similar extent by the 2 Cd compounds. Alcohol dehydrogenase was more strongly affected by CdCl2 than by Cd(DTC)2, although the uptake of Cd was 3-4 times higher in cells incubated with Cd(DTC)2 than in those incubated with CdCl2. The results from the present study show that DTC can increase the transport of Cd into the cell by complex formation with Cd. Compared to CdCl2 the Cd(DTC)2 complex was less toxic as indicated by the biochemical parameters used.

Alcohol Dehydrogenase↗

Comparison of renal toxicity after long-term oral administration of cadmium chloride and cadmium-metallothionein in rats.

There is a clear lack of information on the toxicological risk of dietary intake of cadmium-metallothionein (CdMt). The present study aimed at establishing dose-dependent cadmium (Cd) disposition and to investigate differences in renal toxicity after long-term dietary exposure to CdMt or cadmium chloride (CdCl2) in rats. Male Wistar rats were fed diets containing 0.3, 3, 30, or 90 mg Cd/kg either as CdMt or as CdCl2 for 10 months. In rats fed 30 and 90 mg/kg Cd as CdCl2 the Cd concentrations in intestine, liver, and kidneys were all higher than in rats fed the same doses in the form of CdMt. The kidney/liver Cd concentration ratio was higher with CdMt than with CdCl2. At the lower Cd concentrations (0.3 and 3 mg/kg), no differences in Cd accumulation between CdMt and CdCl2 groups were observed and the kidney/liver Cd ratio was also similar. When based on the amount of CdMt per milligram Cd in the tissue, rats fed CdMt and those fed CdCl2 had a similar relative CdMt concentration in liver and kidney. First signs of renal injury, indicated by an increase of urinary lactate dehydrogenase (LDH) activity, were seen 4 months after exposure to 90 mg/kg Cd as CdCl2. After 8 and 10 months the renal effect of 90 mg/kg Cd as CdCl2 became more pronounced and urinary enzyme activities of LDH, N-acetyl-beta-D-glucosaminidase and alkaline phosphatase were all elevated. The only clinical effect of CdMt at the dose level of 90 mg/kg was a slight increase in urinary gamma-glutamyl transpeptidase activity at 8 and 10 months.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

Cadmium accumulation and metallothionein concentrations after 4-week dietary exposure to cadmium chloride or cadmium-metallothionein in rats.

The distribution of cadmium was examined in rats fed diets containing either cadmium-metallothionein (CdMt) or cadmium chloride (CdCl2) for 4 weeks. The test diets contained 3, 10, or 30 mg Cd/kg diet (3, 10, or 30 ppm) as CdMt or 30 mg Cd/kg diet (30 ppm) as CdCl2. A second study was performed to establish the Cd content in liver and kidneys after exposure to low doses of both CdMt and CdCl2 (1.5 and 8 ppm Cd). The feeding of CdMt resulted in a dose- and time-dependent increase of the Cd concentration in liver, kidneys, and intestinal mucosa. Rats fed 30 ppm CdMt consistently showed less Cd accumulation in liver and intestinal mucosa than did rats fed 30 ppm CdCl2. However, renal accumulation in rats fed 30 ppm was similar until Day 28 regardless of Cd form. At lower dietary Cd levels (1.5 and 8 ppm), relatively more Cd is deposited in the kidneys, although even at these doses the kidney/liver ratio of Cd is still higher with CdMt than with CdCl2. Tissue metallothionein (Mt) levels in the intestinal mucosa were relatively constant but always higher after CdCl2 exposure than after CdMt exposure. Mt levels in both liver and kidney increased after CdCl2 or CdMt exposure during the course of study. Although Mt levels in liver were higher after CdCl2 intake (30 ppm) than after CdMt intake (30 ppm), renal Mt concentrations were the same for both groups. In fact on Day 7, CdMt administration resulted in slightly higher Mt levels than CdCl2 administration, suggesting a direct accumulation of exogenous CdMt in the kidneys. In conclusion, after oral exposure to CdMt in the diet there is a relatively higher Cd accumulation in the kidneys. However, the indirect renal accumulation via redistribution of Cd from the liver might be lower than after CdCl2 exposure. Which of these two phenomena is decisive in the eventual level of renal toxicity of Cd after long-term oral intake could determine the toxicological risk of the chronic intake of biologically incorporated Cd.

Animals↗

Embryotoxicity and in vivo cytogenetic changes following maternal exposure to cadmium chloride in mice.

Cadmium is a well-known teratogen in laboratory animals and a widespread environmental pollutant. The frequencies of sister chromatid exchanges (SCEs), nucleolar organizing regions (NORs) and chromosomal aberrations were analysed in maternal bone marrow and fetal liver and/or lung cells of mice, following maternal treatment with cadmium chloride, on gestational days 8 through 10. The embryotoxic effects and morphological changes on day 18 fetuses were also studied. Cadmium chloride is readily transferred across the placenta and significant levels were detected in both the placenta and fetus. No significant changes in the frequencies of SCEs or NORs in maternal and fetal cells were observed following exposure to cadmium chloride. Fetal tissues showed mitotic inhibition at the highest dose levels (8.4 and 11.4 mg/kg, b.w.). Maternal treatment with cadmium chloride increased embryonic resorptions and fetal lethality, as well as reduced placental weight; however, it did not produce significant chromosomal changes except at the highest dose level (11.4 mg/kg).

Abnormalities, Drug-Induced↗

Assessment of renal toxicity by analysis of regeneration of tubular epithelium in rats given low-dose cadmium chloride or cadmium-polluted rice for 22 months.

To determine whether low-dose oral administration of cadmium (Cd) induces renal toxicity, six groups of female Sprague-Dawley rats were fed a diet containing low amounts of CdCl2 or Cd-polluted rice at concentrations up to 40 ppm, and were killed after 12, 18, and 22 months (experiment 1). In addition to the determination of cortical Cd levels and histopathological assessment of kidneys, labeling indices (LIs) for proliferating cell nuclear antigen (PCNA) in the renal cortical tubular epithelium of Cd-treated rats were determined as a measure of regenerative activity. For comparison, the kidneys of rats given diets containing small to large amounts of CdCl2 up to 600 ppm for 4 months were similarly examined (experiment 2). Animals in experiment 1 demonstrated spontaneous chronic nephropathy and fluctuation in the tubular PCNA LI, but these findings were not correlated with renal Cd levels at 22 months. PCNA LI on the other hand, appeared to be linked to the severity of chronic nephropathy. In experiment 2, levels of CdCl2 of 200 ppm or more clearly induced degeneration and apoptosis of proximal tubules with high correlations between renal Cd levels, PCNA LI, and the severity of tubular degeneration. The results demonstrated that, in contrast to high-dose Cd administration, treatment with 40 ppm or less for 22 months did not influence tubular regeneration as a component of nonspecific chronic nephropathy, suggesting that long-term oral administration of low levels of Cd does not injure renal tubules in female rats.

Animals↗