The regulation mechanism of protein kinase Cδ on arsenic liver injury caused by coal-burning / 中华预防医学杂志

<p><b>OBJECTIVE</b>To investigate the effects of mRNA transcriptional and protein expressions of protein kinase Cδ (PKCδ) on the development of arsenic liver injury caused by coal-burning.</p><p><b>METHODS</b>Population study:133 arsenic exposures were selected as arsenic exposure groups including the ward non-patient group (25 cases) , no obvious hepatopathy group (38 cases) , mild (43 cases) and moderate to severe hepatopathy group (27 cases) from the area with endemic arsenism in Guizhou province. Another 34 healthy residents were selected as the control group in non-arsenic pollution village. The urine and peripheral blood were collected from the subjects. The arsenic contents in urine and mRNA expressions of PKCδ in peripheral blood were detected. Animal experiment study:thirty wistar rats were randomly by random number table divided into control group, drinking water arsenic poisoning group and coal-burning arsenic poisoning group (i.e., low, medium and high arsenic contaminated grain group) by random number table method, including 6 rats in each group. The control group was fed normally for 3 months, drinking water arsenic poisoning group and coal-burning arsenic poisoning groups were fed respectively with 10 mg/kg As2O3 solution and different concentrations (25, 50 and 100 mg/kg) of arsenic-containing feed which was persisted 3 months. The arsenic contents in urine, mRNA expression levels of PKCδ in peripheral blood and liver tissue and the protein expression levels of phosphorylated protein kinase Cδ(pPKCδ) in liver tissue were detected.</p><p><b>RESULTS</b>The median(quartile) of arsenic contents in urine were 25.58 (18.62-40.73), 56.66 (38.93-76.77), 64.90 (39.55- 98.37) and 75.47 (41.30-109.70) µg/g Cr respectively for the non-patient group, no obvious hepatopathy group, mild and moderate to severe hepatopathy group. The levels were higher than that in the control group (23.34 (17.84-37.45) µg/g Cr) (P < 0.05), except for the ward non-patient group. The arsenic contents in rat urine were 2223.61 (472.98-3976.73), 701.16 (194.01-1300.27), 1060.94 (246.33-2585.47) and 3101.11 (1919.97-5407.07) µg/g Cr, respectively for the drinking water arsenic poisoning group, the low, medium and high dosage arsenic grain contamination groups, all higher than that in the control group (94.32 (22.65-195.25) µg/g Cr) (P < 0.05) . The protein expressions of pPKCδ in liver tissue were 324.83 ± 25.06, 278.50 ± 30.57, 308.83 ± 34.67 and 326.33 ± 35.09, which were significantly higher than that in the control group (240.17 ± 28.07) (P < 0.05) . The protein expression levels of pPKCδ in liver cell membrane were 0.49 ± 0.06,0.33 ± 0.05,0.37 ± 0.06 and 0.50 ± 0.08, which were significantly higher than that in the control group (0.28 ± 0.04) (P < 0.05) . The protein expression levels of pPKCδ in liver cell cytoplasm were 0.38 ± 0.06,0.31 ± 0.05, 0.35 ± 0.05 and 0.36 ± 0.05, which were significantly higher than that in the control group (0.24 ± 0.05) (P < 0.05).</p><p><b>CONCLUSION</b>The arsenic may regulate protein expressions of pPKCδ and induce its membrane translocation, and cause the development of arsenic liver injury caused by coal-burning.</p>

The establishment of the arsenic poisoning rats model caused by corn flour baked by high-arsenic coal / 中华预防医学杂志

<p><b>OBJECTIVE</b>To establish coal arsenic poisoning rat model by feeding the rats with the corn powder baked by high arsenic coal as the main raw material.</p><p><b>METHODS</b>Fifty Wistar rats, healthy, were randomly divided into 5 groups according to the figures of their weights, including control group, drinking arsenic poisoning water group, low, medium and high arsenic contaminated grain group, 10 rats for each.Rats in control group and drinking arsenic poisoning water group were fed with standard feed without any arsenic containing. Rats in water group would drink 100 mg/L As2O3 solution and the rats in arsenic grain groups would be fed with the arsenic contaminated grain at the dose of 25, 50 and 100 mg/kg, respectively. The duration would last for 3 months.General situation and weight were observed. At the same time, the arsenic contents of urine, hair, liver and kidney of the rats in each group were detected, as well as the histopathology changes of liver and kidney, and the ultra structure of liver was observed.</p><p><b>RESULTS</b>The arsenic contents of urine (median(min-max)) of the rats in the arsenic water group, low, medium and high arsenic grain groups were separately 3055.59 (722.43-6389.05), 635.96(367.85-1551.31), 1453.84 (593.27-5302.94) and 3101.11 (666.64-6858.61) µg/g Cr; while the arsenic contents of hair of the rats in the above groups were separately (23.07 ± 10.38), (8.87 ± 3.31), (12.43 ± 6.65) and (25.68 ± 7.16) µg/g; the arsenic contents of liver of the rats in the above groups were separately (5.68 ± 3.13), (2.64 ± 1.52), (3.89 ± 1.76) and (5.34 ± 2.78) µg/g; and the arsenic contents of kidney were separately (6.90 ± 1.94), (3.48 ± 1.96), (5.03 ± 2.08) and (7.02 ± 1.62) µg/g; which were all significantly higher than those in the control group (86.70 (49.71-106.104) µg/g Cr,(1.28 ± 0.37) µg/g, (1.01 ± 0.34) µg/g and (1.82 ± 1.09) µg/g, respectively). The difference showed significance (P < 0.05). Under electron microscope detection, we observed the reduction of mitochondrial, the blurred mitochondrial cristae, some disappeared ridges, the reduced rough endoplasmic reticulum, and irregular uneven nuclear in the liver cells of rats in arsenic contaminated grain group. The contents of aspartate transaminase (AST) and total bile acid (TBA) in medium and high arsenic contaminated grain group were respectively (196.17 ± 46.18), (212.40 ± 35.14) U/L and (11.74 ± 4.07), (19.19 ± 4.68)µmol/L, which were higher than it in the control group (separately (143.10 ± 29.13) U/L and (6.23 ± 2.95)µmol/L). The contents of glutathione-S-transferases(GST), γ-glutamyltranspeptidase (GGT)and blood urea nitrogen (BUN)in high arsenic contaminated grain group were separately (196.21 ± 47.38)U/L, (1.71 ± 0.66)U/L, (9.54 ± 1.95)mmol/L, which were higher than that in the control group ((134.93 ± 24.80 )U/L, (0.75 ± 0.36)U/L, (7.67 ± 1.02)mmol/L, respectively). The contents of cholinesterase (CHE) in low, medium and high arsenic contaminated grain group were separately (259.90 ± 52.71)U/L, (263.44 ± 66.06)U/L and (244.90 ± 36.14)U/L, the contents of total protein(TP) in rats of high arsenic contaminated grain group were (62.64 ± 5.50)g/L, which was all lower than that in the control group ((448.33 ± 59.67)U/L, (69.38 ± 4.24)g/L, respectively). The contents of TBA in high arsenic contaminated grain group ( (19.19 ± 4.68) µmol/L) was higher than that in drinking water arsenic poisoning group ((15.15 ± 2.64)µmol/L). The differences of the above indexes were all significant (P < 0.05).</p><p><b>CONCLUSION</b>The results showed the arsenic poisoning rat model produced by coal-burning were successfully established.</p>