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Objective To investigate the effect of hot spring baths on human immune function by analyzing the changes of immunoglobulins and complements in serum of residents after hot spring baths in order to provide a theoretical reference for the therapeutic effect of hot spring bathing. Methods After physical examination, 421 volunteers from five hot spring areas with three types of hot springs(temperature type hot springs, metasilicic acid type hot springs, and warm mineral spring type hot springs)in Guizhou Province were selected as the subjects. Under the guidance of professionals, the volunteers took a hot spring bath with the whole body immersed for four weeks, once a day, 5 times a week and 40-50 minutes each time. Finally, 311 volunteers completed the standard bath required by this study. The transmission immunoturbidimetric method was used to determine the content of immunoglobulins reflecting mucosal anti-infective immunity(IgA), anti-pathogenic microorganisms(IgG), recent infections(IgM)and the level of important immune effect factors(C3, C4)in the serum. Paired T test was used to compare the changes of serum immunoglobulin and complement before and after the hot spring bath therapy. Results Before the hot spring baths, the content of serum IgG, IgA, IgM, and complements C3 and C4 was(12.169±2.358)g/L, (2.285±0.891)g/L, (1.430±0.660)g/L, (1.224±0.186)g/L, and(0.257±0.073)g/L, respectively. After the hot spring baths, the content of serum IgG, IgA, IgM, and complements C3 and C4 was(12.769±2.984)g/L, (2.397±0.909)g/L, (1.497±0.715)g/L, (1.242±0.169)g/L, and(0.266±0.074)g/L, respectively.Comparison of results of different types of hot springs showed that warm mineral type of hot springs and metasilicic acid type of hot springs could significantly increase the serum levels of main immunoglobulins IgG and IgA(P < 0.05), while water temperature type of hot springs could increase the serum IgA content of the population(P < 0.05), but the effect on IgG was not significant(P > 0.05). Compared with before the bath intervention, the level of complement C4 in the serum increased in the population after the intervention of metasilicic acid type of hot springs and water temperature type of hot springs(P < 0.05). Conclusion Hot spring bathing can enhance the body's humoral immune function. Given that IgG is the most important anti-pathogenic microorganism antibody in body fluids, the result suggests that metasilicic acid hot spring and warm mineral hot spring are better than pure water temperature hot spring in terms of improving the body's humoral immune function.
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Objective To analyze the changes of major and trace elements in urine before and after hot spring bathing, and to explore the effect of hot spring bathing on element metabolism, so as to provide theoretical reference for the physiotherapeutic efficacy of hot spring bathing. Methods The content of Ca, K, Mg, Na, P, S, Sr, Zn, B, Mn, Ni, V, Se, Co, Cr, Cu, Fe, Mo, As, Cd, Hg, Li, Pb and Al in warm mineral springs, metasilicic springs and mineral springs in Guizhou Province was determined by ICP-MS. On the basis of physical examination, 421 people in hot spring areas of Guizhou Province were selected as the subjects. Under the guidance of professionals, the volunteers took a hot spring bath with the whole body immersed for four weeks, once a day, five times a week, for 40-50 minutes each time. Finally, 311 volunteers completed the standard bath required by this study. The content of major elements(Ca, K, Mg, Na, P, and S), essential trace elements(Co, Cr, Cu, Fe, Mo, Se, Sr, and Zn), possibly essential trace elements(B, Mn, Ni, and V)and potentially toxic elements(Al, As, Cd, Hg, Li, and Pb)in urine was analyzed by ICP-MS. Wilcoxon test was used to compare the differences of various elements in urine before and after bathing. Results The water of the warm mineral spring pool mainly contained Mo, Sr, Zn, B, Al, and Pb. The metasilicic acid water mainly contained Cu, V, and As. The water of the mineral spring bubble pool mainly contained Ca, K, Mg, S, Cr, Fe, Se, Mn, Ni, and Li. Compared with before intervention, the content of major elements(Ca, K, Mg, S), essential trace elements(Co, Cr, Cu, Fe, Mo, Se, Zn)and possibly essential trace elements(B, Mn, Ni, V)significantly increased, and the content of potential toxic elements(Al, Li, Pb)significantly decreased after intervention(all P < 0.05). The results showed that the content of P, S, Co, Cr, Mo, Se, Zn, Mn and Ni increased significantly and the content of Hg decreased significantly after metasilicic acid hot spring bathing compared with that before bathing(all P < 0.05). After warm mineral hot spring bathing, the content of Ca, Mg, S and Zn increased significantly, while the content of Al and Pb decreased significantly(all P < 0.05). The content of Mg, S, Co, Cr, Se and Ni increased significantly and the content of Al decreased significantly(all P < 0.05). Conclusion There are many kinds of mineral elements in hot springs in Guizhou Province. After hot spring bathing, the essential trace elements and possible essential trace elements in human body increased, and the potential toxic elements decreased, but there was no gender difference.
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<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>