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Objective To explore the long-term effect of endemic arsenism on oxidative stress and immune function, and to provide scientific basis for prevention and treatment of the disease in the areas. Methods In 2009, Using cluster sampling and typical investigation, the cross-sectional study was completed. The patient groups and the internal control group were selected in the arsenism areas after 5 years quality improvement of drinking water(Silizhuang village, Daying village and Gucheng village in Shanyin county, Gucheng city, Shanxi province) and they were divided into mild, moderate, severe case and internal control groups, respectively. The external control group was selected in a non-arsenism area(Yangzhuang village in Heshengbu city). The Oxidative stress indicators were determined and analyzed [serum superoxide dismutase (SOD) activity was determined with xanthine oxidase method, glutathione peroxidase(GSH-Px) activity was determined with 2-thio-2-nitrobenzoic acid method, and mmuuity malondisldohyde(MDA) levels was determined with thiobarbituric acid method]. The immune function was determined and analyzed [immunoglobulin G (IgG) was determined with radioimmunoassay method, and serum lysozyme was determined with turbidimetric method]. Results A total of 252 people were surveyed, in which the external control group, the internal control group, mild, moderate and severe patient groups were 56, 57, 49,44 and 46, respectively. Serum SOD activities were (72.19 ± 11.75), (66.96 ± 12.02), (49.79±11.07), (48.54 ±10.56) and (47.68 ± 10.68)kU/L, respectively. The difference of serum SOD activities between the groups was statistically significant(F = 52.42, P ＜ 0.01 ). Serum SOD activities in the external control group were significantly higher than other groups (all P ＜ 0.05). The value in the internal control group was significantly higher than the 3patient groups (all P ＜ 0.05). There were no significant differences between the case groups (P ＞ 0.05). Serum GSH-Px activities of the five groups were (197.41 ± 38.54), (195.02 ± 31.93), (187.26 ± 28.22), (187.24 ± 25.40),(186.88 ± 21.84)U/mg, respectively, and the difference between the groups was not significant(H = 4.21, P ＞0.05). Serum MDA levels of the five groups were (4.51 ± 2.14), (5.88 ± 2.00), (6.44 ± 2.83), (5.89 ± 2.57),(5.88 ± 2.40)μ mol/L, respectively, and the difference between the groups was statistically significant(F = 3.36,P ＜ 0.05). The external control group was significantly lower than other groups(all P ＜ 0.05). No significant difference was observed between other groups(all P ＞ 0.05). Serum IgG levels were(11.16 ± 2.08), (8.15 ± 1.44), (8.77 ±2.54), (9.19 ± 1.97), (8.44 ± 2.52)g/L, respectively, and the difference between the groups was statistically significant(H = 52.92, P ＜ 0.01 ). The external control group was significantly higher than other groups(all P ＜0.05). No significant difference was observed between other groups(all P ＞ 0.05). Serum lysozyme levels were (13.57 ± 5.16), (10.05 ± 3.96), (8.78 ± 3.35), (8.72 ± 3.76), (9.38 ± 4.26)mg/L, respectively, and the difference between the groups was statistically significant (H = 35.00, P ＜ 0.01 ). The external control group was significantly higher than other groups(all P ＜ 0.05). No significant difference was observed between other groups(all P ＞ 0.05). Conclusions The effect of arsenic on the body's oxidative stress response and immune function persists after 5 years of drinking low arsenic water. In addition to intensify arsenic removal from drinking water, it should also strengthen the monitoring of population's health in the diseased areas.
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Objective To explore into the condition of fluoride content of the drinking water and the present status of water-improving projects in the endemic fluomsis areas in Shanxi province,and to provide the evidence for making scientific and effective tactics in prevention and control.Methods In 2007,according to "The National Technical Scheme for Endemic Disease Control",screening for drinking water fluoride content was carried out in non-improving water villages of 15 counties(cities,districts).The investigation of all water-improving projects was carried out in 10 counties(cities).The fluoride content in drinking water was determined by fluoride selective ion electrode(GB/T 8538-1995).Results Screening for drinking water fluoride content was carried out in 969 non-improving water villages in 15 counties(cities,districts).Average water fluoride content was≤1.0 mg/L in 497 villages,accounting for 51.29%(497/969).Average water fluoride content was>1.0 mg/L in 472 villages.accounting for 48.71%(472/969).The overall standard drinking water fluoride content was mainlv>1.0-4.0mg/L,and the maximum average water fluoride content was 8.96 mg/L.The investigation of 290 water-improving projects was carried out in 10 counties(cities).Among 290 water-improving projects 213 water-improving projects were running normally,accounting for 73.45%(213/290);77 water-improving projects were running abnormally,accounting for 26.55%(77/290).Water fluoride content was≤1.0 mg/L in 158 projects,accounting for 54.48%(158/290).Water fluoride content was>1.0 mg/L in 132 projects,accounting for 45.52%(132/290).The maximal water fluoride content was 5.20 mg/L.Conclusions The situation of drinking water fluoride content over the national standard is serious in Shanxi province.The qualification rate was lower for the fluoride content of water-improving projects.Therefore,we should strength water-improving projects to raise the effectiveness of prevention and treatment and assure their quality.
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Objective To investigate the relationship between arsenic in drinking water and skin lesions in endemic arsenism area in Shanyin County of Shanxi Province,in order to provide epidemiologic data for further arsenism research.Methods One hundred and eighty-nine endemic arsenism patients and 59 controls were randomly selected in 17 endemic amenism countries in Shanyin County of Shanxi Province.The content of arsenic in drinking water which wa8 collected indoom was half-quantitatively screened by a kit made by Chinese Center for Disease Control and Prevention,then quantitatively determined by HPLC-ICP-MS.Patients of endemic arsenism were diagnosed by "The Standard of Diagnosis for Endemic Amenism"(WS/T 211-2001).Results There were 64.9% (87/134)samples above the arsenic level(50μg/L)of drinking water and the median value of arsenic in drinking water was 91.43 μg/L in 134 water samples.The OR(95%CI)value between arsenic in drinking water and hyperkeratosis,hyperpigmentation,depigmentation was 2.46(1.22-4.94),3.34(1.50～7.44)and 2.86(1.50-5.46),respectively.The prevalence of hyperkeratosis,hyperpigmentation and depigmentation increased,as the arsenic in drinking water increased(≤10,≤50,≤200,＞200μg/L),especially in＞200μg/L group(OR=6.15,13.96,11.41,P＜0.05).The arsenic level in drinking water of Ⅲ degree of depigmentation patients(318.300μg/L)was higher(P＜0.05)than that of 0,Ⅰ and Ⅱ degree groups(86.670,131.800,1 10.590μg/L,P＜0.05).Conclusions Shanyin County is a medial arsenic pollution area. Arsenic in drinking water is considered as a risk factor of skin lesion. The degree of skin lesions increased,as the arsenic in drinking water increased.
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Objective To become aware of the present distribution of drinking water source with high fluoride in endemic fluorosis disease areas in Shanxi Province, and to provide the evidence for making scientific and effective tactics in prevention and control. Methods According to "The National Technical Scheme for Endemic Disease Control" in the year 2004 to 2006, the investigation points were selected in 60 counties at 8 cities of Shanxi Province. The fluoride levels of water were determined by fluoride selective ion electrode. Results The fluoride content of water was determined in 2990 villages in 60 counties. Water fluorides content of 1658 villages were above 1.00 mg/L, accounted for 55.45%(1658/2990). The highest water fluoride content was 9.72 mg/L. Villages with high fluoride water in Taiyuan, Datong, Xinding, Linfen, Yuncheng basins accounted for 89.63% (1486/1658) among villages with high fluoride in Shanxi Province. In Shanxi Province the villages with high fluoride water were mainly distributed over 5 basins and scattered on the other areas. The distribution of drinking water source with high fluoride were different in 5 basins(H=316.10, P<0.05). The Water fluorides content in Datong basin(2.32 mg/L) was significantly higher than that of the other basins (P<0.05) and the ratio of drinking water fluoride levels under the national standard was 81.16%(336/414) in Datong basin. Conclusions Drinking water source with high fluoride are widespread distributed in Shanxi Province and mainly distributed in 5 basins. The situation of drinking water fluoride levels under the national standard is serious. The task of prevention and control for endemic fluorosis is still arduous. Therefore, we should strength water improving to raise the effect of prevention and treatment.
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<p><b>OBJECTIVE</b>To explore the level and feature of neonate deformity in water arsenic exposure areas, as to finding out an evidence for the study and prevention of the arsenic exposure.</p><p><b>METHODS</b>The birth situation of neonate was surveyed from 1998 to 2004 in water arsenic exposure areas according to cross-sectional survey. The results were classified in accordance with ICD-10 and common surveillance of china. The population of Shanyin County served as the common people and the data were analyzed by SPSS 11.5 for windows.</p><p><b>RESULTS</b>The neonates surveyed were 2467 cases. There were 49 neonates deformity found in this investigation, giving a neonate deformity rate of 198.62 per 10,000 cases, which was shown significantly higher in water arsenic exposure areas than in the normal (U = 3.23, P < 0.01), with types of nervous system deformity, limbs deformity and congenital heart disease as in system classification. There was no significant difference of deformity rate in different sex neonates (chi2 = 0.32, P > 0.05).</p><p><b>CONCLUSION</b>The drinking high-arsenic water over a long period of time should be a risk factor of neonate deformity. Prevention and treatment of endemic arsenic exposure should be urgently needed.</p>