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This study aims to evaluate the protective effect of grape seed proanthocyanidin extract (GSPE) on cadmium (Cd)-induced testicular apoptosis, endothelial nitric oxide synthases (eNOS) expression, and toxicity in rats. A total of 24 male Wistar rats were divided into four groups, namely, control, Cd (2.5 mg/kg), Cd + GSPE (100 mg/kg/day), and GSPE. Spermatogenesis and mean seminiferous tubule diameter were significantly decreased in the Cd groups. Furthermore, the GSPE-treated animals showed an improved histological appearance in the Cd group. The immunoreactivity of eNOS and the number of apoptotic cells were increased in Cd group. Our data indicate a significant reduction of terminal deoxynucleotide transferase-mediated 2'-deoxyuridine 5'-triphosphate nick end-labeling staining and a decrease in the expression of eNOS in the testes tissue of the Cd group treated with GSPE therapy. Therefore, our results suggest that GSPE acts as a potent protective agent against Cd-induced testicular toxicity in rats., (© The Author(s) 2015.)

The present study was carried out to evaluate the neuroprotective effect of quercetin (QE) in protecting the cadmium (Cd)-induced neuronal injury in frontal cortex of rats. A total of 30 adult male Sprague-Dawley rats were randomly divided into three groups of 10 animals each: control, Cd treated and Cd treated with QE. The Cd-treated group was injected subcutaneously with cadmium chloride (CdCl2) dissolved in saline at a dose of 2 ml/kg/day for 30 days, resulting in a dosage of 1 mg/kg Cd. The rats in QE-treated groups were given QE (15 mg/kg body weight) once a day intraperitoneally starting 2 days prior to Cd injection, during the study period. Rats were sacrificed at the end of the study and the frontal cortex tissues were removed for biochemical and histopathological investigation. To date, there is no available information on the effect of QE on neuronal injury after Cd exposure. Rats intoxicated with Cd for 30 days, significantly increased tissue malondialdehyde (MDA) levels and significantly decreased enzymatic antioxidants superoxide dismutase, glutathione peroxidase and catalase in the frontal cortex tissue. Administration of QE with Cd significantly diminished the levels of MDA and significantly elevated the levels of enzymatic antioxidants in the frontal cortex tissue. The histopathological studies in the brain of rats also supported that QE markedly reduced the Cd-induced histopathological changes and well preserved the normal histological architecture of the frontal cortex tissue. The caspase-3 immunopositivity was increased in degenerating neurons of the Cd group. Treatment with QE markedly reduced the immunoreactivity of degenerating neurons. In conclusion, the results of the current study suggest that QE may be beneficial in combating the Cd-induced neurotoxicity in the brain of rats. We believe that further preclinical research into the utility of QE may indicate its usefulness as a potential treatment for neurodegeneration after Cd exposure in rats., (© The Author(s) 2013.)

Cadmium (Cd) is one of the most dangerous occupational and environmental toxins. The objective of the present study is to examine the potential prophylactic effects of phytic acid (PA) on thyroid hormones of male rats intoxicated with Cd. The male albino rats were divided into five groups: group I (control) was fed with the basal diet, group II was intoxicated with Cd in drinking water, groups III, IV, and V were intoxicated with Cd in drinking water and fed with the diet containing 3.5, 7, and 10 g of PA/kg, respectively. The results indicated that the serum calcium, iron (Fe), and total Fe binding capacity levels and serum T3 and T4 in Cd-treated rats of group II were decreased when compared with the control group, while PA-administered groups with Cd showed a significant improvement when compared with the Cd-treated rats only. Serum thyroid stimulating hormone (TSH) level was significantly increased in Cd-treated rats compared with the control group, while the addition of PA in diet decreased the high levels of TSH. These results indicated a prophylactic effect of PA against Cd-induced toxicity in rats., (© The Author(s) 2013.)

The highly conserved human and mouse SLC39A8 gene encodes the divalent cation/bicarbonate symporter ZIP8 expressed ubiquitously in most cell types. Our bacterial artificial chromosome-transgenic BTZIP8-3 line has 3 additional copies of the Slc39a8 gene in addition to its constitutive diploid pair found in wild-type (WT) mice. In liver, kidney, lung, testis, gastrointestinal tract, and brain, BTZIP8-3 mice are known to express ∼2.5 times greater amounts of ZIP8, compared with WT mice. Herein we administered cadmium chloride (CdCl₂) in drinking water (100 mg/L through week 2, 200 mg/L through week 4, 400 mg/L through week 8, 800 mg/L through week 12, and 1600 mg/L through week 20, when the experiment was concluded). We postulated that Cd uptake and distribution--and, therefore, toxicity in certain tissues--would be enhanced in BTZIP8-3, compared with WT mice. BTZIP8-3 and WT groups ingested comparable amounts of Cd. Compared with WT, BTZIP8-3 mice showed tissue specific: increases in Cd, zinc, and manganese content and decreases in calcium content. Both Cd-exposed BTZIP8-3 and WT were similar in lower urinary pH; increased plasma alanine and aspartate aminotransferase activities; elevated iron and copper content in liver, kidney, lung, and testis; and higher blood urea nitrogen and kidney weight. Histological changes in liver, kidney, lung, and testis were minimal. In summary, at the daily oral Cd exposures chosen for this study, 5 versus 2 Slc39a8 gene copies result in no differences in Cd toxicity but do cause differences in tissue-specific content of Cd, zinc, manganese, calcium, iron, and copper.

Dietary fiber can affect cadmium (Cd) absorption and toxicity, but the effect appears to depend on the type of dietary fiber. The aim of the present study was to compare the effect of dietary sources containing distinct amounts of soluble and insoluble fiber on Cd absorption, accumulation and toxicity in growing rats. The absorption of essential macrominerals (Ca, P and Mg) was also evaluated. Animals received a nutritionally balanced diet with cellulose (cel - control), wheat bran or flaxseed as the fiber source with 0 or 50 mg Cd kg(-1) diet, during 30 days. Cd exposure reduced body weight gain, feed efficiency ratio, epididymal fat relative weight and liver relative weight, and increased plasma alanine aminotransferase activity in all fiber groups. The apparent Cd absorption was similar among Cd-groups, but the flax-Cd group had a higher hepatic and renal Cd concentration. Cd decreased the absorption of Ca and P, and increased Mg absorption in the wheat bran and flaxseed groups, but not in the cel group. Although the different fiber sources investigated had no effect on Cd toxicity, the major soluble fiber source, flaxseed, increased Cd retention. Thus, caution should be taken in the intake of flaxseed by Cd-exposed populations.

The present research aimed to characterize the potential efficiency of two chelators after cadmium administration for 60 days following two dose levels of 20 and 40 mg/kg body weight daily to male rats. However, the hypothesis that the two chelators might be more efficient as combined therapy than as single therapy in removing cadmium from the body was considered. In this way, two known chelators deferasirox and deferiprone (L(1)) were chosen and tested in the acute rat model. Two chelators were given orally as a single or combined therapy for the period of a week. Cadmium and iron concentrations in various tissues were determined by graphite furnace and flame atomic absorption spectrometry methods, respectively. The combined chelation therapy results show that Deferasirox and L(1) are able to remove cadmium ions from the body while iron concentration returned to the normal level and symptoms are also decreased.

Although cadmium (Cd) is extensively used for nickel-cadmium battery production, few recent reports are available on the effect of this toxic metal on the imbalance of biometals in occupational exposure. The current study was carried out to determine the Cd level and its effect on the content of bioelements: zinc, cooper, magnesium, and iron in blood and urine of workers exposed to Cd during nickel-cadmium battery production. beta(2)-microglobulins (beta(2)-MG), as indicators of kidney damage, were determined in urine.The study group comprised 32 male nickel-cadmium battery workers, and the control group had 15 male construction workers with no history of Cd exposure. Levels of Cd and bioelements were determined in blood and urine by atomic absorption spectrophotometry.Cd concentration in blood of exposed workers was around 10 microg/L and in urine ranged from 1.93 to 8.76 microg/g creatinine (cr). Urine Cd concentration was significantly higher in exposed workers than in the controls, although no statistical difference in beta(2)-MG content was observed in urine between the two groups. Blood Zn and Mg level were significantly reduced and urine Zn level was increased in Cd-exposed group when compared with controls.The mean Cd concentrations in blood and urine did not exceed the recommended reference values of 10 microg/L in blood and 10 microg/g cr in urine. Cd exposure resulted in disturbances of Zn in blood and urine and Mg in blood but had no effect on Cu and Fe content in biological fluids.

Cadmium (Cd) has been identified as the etiologic agent of itai-itai disease. The purpose of this study was to investigate whether chronic Cd exposure affects bone metabolism in a male rat model and to estimate the bone mineral density (BMD) differences in lumbar and femoral bone because of Cd exposure. Six-week-old male Hos Donryu rats were used in this experiment. Cadmium was administered at a dose of 200 ppm to rats in the diet to produce experimental chronic Cd poisoning. Bone mineral density was measured using dual-energy X-ray absorptiometry (DEXA) with a high-resolution scan collimator (0.25 mm diameter) (Hologic QDR-2000). The Cd content in renal tissue reached a critical concentration of 128.42 +/- 14.38 microg/g 10 months after the administration of the element (Table 3). The average blood urea nitrogen (BUN) value was increased throughout the period of the experiment, and the serum creatinine value of the experimental group showed an increase after 2 months of Cd administration (0.46 +/- 0.09 mg/dL). The concentration of urinary calcium changed in the experimental group after exposure to Cd for 12 months (15.4 +/- 0.13 mg/dL). DEXA showed a greater reduction in the bone mineral density of the 5th vertebral body (L5) in rats that had ingested Cd for 4 months (0.359 +/- 0.013 g/cm2) than in control rats (0.372 +/- 0.012 g/cm2, P < 0.01). On the contrary, the difference in bone mineral content between rats ingesting Cd for 6-8 months and control rats was not significant. However, significant reductions in bone mineral content were again noted in rats that had ingested Cd for 12 months (0.339 +/- 0.023 g/cm2) compared with the control group (0.385 +/- 0.012 g/cm2, P < 0.01). The bone mineral density of the right femoral bone in control rats was 0.328 +/- 0.018 g/cm2 and that in experimental rats was 0.306 +/- 0.012 g/cm2, and a meaningful difference was recognized (P < 0.05). Histological examination of the rats exposed to Cd for 12 months showed that the 5th lumbar vertebral body (L5) exhibited osteomalacia. The results of our studies show that Cd stimulated a loss of bone mineral at an early stage to a great extent in male rats. In the examination of male rats, bone injury and renal functional disorder were encountered simultaneously. This study suggested that osteomalacia was induced by a direct action of Cd on the bone through abnormal calcium homeostasis at an early stage in male rats.

An indirect immunoperoxidase staining technique was employed to localize the heavy metal binding protein, metallothionein, in rat liver and kidney. Immunostaining for metallothionein was observed in all hepatocytes and most renal tubular cells. This protein was not detectable, however, in cell types such as endothelial or connective tissue cells, indicating that metallothionein synthesis or accumulation is tissue- and cell-type specific. Hepatocytes from cadmium-exposed animals showed increased staining for metallothionein. The presence of metallothionein was also seen extracellularly within the liver sinusoids and renal tubules in both normal and cadmium-exposed animals, suggesting transport and excretion, respectively, of this protein.