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Objective:To understand the contents of edible salt iodine and urinary iodine of children and pregnant women in Yunnan Province, and to evaluate the iodine nutrition status, so as to provide a basis for scientific prevention and treatment of iodine deficiency disorders (IDD).Methods:From November to December 2020, one county (city) was selected from each prefecture (city), two townships (towns and streets) were selected from each county (city) and two villages (neighborhood committees) were selected from each township (town and street) from each of the 16 prefectures (cities) in Yunnan Province as the investigation sites. A total of 20 non-boarding children (male and female balanced) aged 8 - 10 years old were selected from each primary school in each village (neighborhood committee) to collect salt and urine samples. A total of 80 children were investigated in each county (city). A total of 20 pregnant women were selected from each township (town and street) to collect salt and urine samples. A total of 40 pregnant women were investigated in each county (city). All salt samples and urine samples were tested for iodine contents.Results:A total of 2 009 salt samples and 2 041 urine samples (1 375 for children, 666 for pregnant women) were collected from children aged 8 - 10 years old and pregnant women in 16 counties (cities) of Yunnan Province. Among them, the median salt iodine was 26.0 mg/kg, the coverage rate of iodized salt was 100.0% (2 009/2 009), the qualified rate of iodized salt was 98.7% (1 982/2 009), and the consumption rate of qualified iodized salt was 98.7% (1 982/2 009). The difference of salt iodine content in key populations in different counties (cities) was statistically significant ( H = 258.98, P < 0.01). The median urinary iodine of children aged 8 - 10 years old was 188.5 μg/L. There was statistically significant difference in urinary iodine content among children of different ages ( H = 29.45, P < 0.01), but there was no statistically significant difference in urinary iodine content among children of different genders ( H = 1.43, P > 0.05). In addition, the median urinary iodine of pregnant women was 141.9 μg/L, 52.1% (347/666) was < 150 μg/L. There was statistically significant difference in urinary iodine content of pregnant women in different counties (cities, H = 88.32, P < 0.01). Conclusions:The qualified rate of iodized salt, the coverage rate of iodized salt and the consumption rate of qualified iodized salt in key populations of Yunnan Province are more than 90%, and the iodized salt supply is good. Iodine nutrition of children aged 8 - 10 years old is at an appropriate level (100 - 199 μg/L); iodine nutrition of pregnant women is in an state of iodine deficiency ( < 150 μg/L). It is suggested to strengthen IDD monitoring and health education among key populations, improve residents' awareness of disease prevention, and make scientific iodine supplementation.
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Objective:To accurately grasp the current status of water iodine distribution in environmental of Yunnan Province, and provide a basis for scientific iodine supplementation.Methods:In 2017, according to the "National Drinking Water Iodine Content Survey Program", a survey of water iodine content was conducted in townships. In 2018, a search survey was carried out for administrative villages with water samples of iodine content > 40 μg/L in drinking water found in previous surveys. In centralized water supply villages, 2 samples of end water were collected. In decentralized or partially decentralized water supply villages, each village was divided into 5 parts: east, south, west, north and center. In villages with more than 50 water sources, 10% of the water sources were selected from each part; villages with less than 50 water sources, one water source was selected from each part; villages with less than 5 water sources, all the water sources were selected to determine the water iodine content. At the same time, the mode of water supply and demographic data were investigated.Results:At the township level water iodine survey, a total of 24 589 water samples were collected from 1 389 townships in 129 counties of 16 prefectures (cities). The median water iodine content of township was 1.3 μg/L, ranging 0.0 - 9.3 μg/L. The population covered by the survey accounted for 53.94% (25 013 804/46 371 207) of the total population of the province. According to the survey results of high iodine villages, 93 administrative villages in 68 townships of 37 counties in 12 prefectures (cities) were surveyed, covering 40 940 households and 208 880 people. A total of 761 samples of drinking water were tested, and the median water iodine content of administrative villages was 1.3 μg/L (ranging 0.0 - 196.8 μg/L). There were 2 administrative villages with iodine higher than 100 μg/L, which were Xiaobona Administrative Village (145.8 μg/L) in Liuchang Township, Xiangyun County, and Dasongshu Administrative Village (196.8 μg/L) in Yangchang Township, Xuanwei City.Conclusions:The iodine content of water in Yunnan Province is generally low, which belongs to the area of environmental iodine deficiency. For the high iodine villages, further investigation should be carried out to clarify the prevention and control measures.
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Objective To conduct an epidemiological investigation on a case of familial arsenic poisoning in Yunnan Province,to find arsenic poisoning source and create a archive of typical cases,in order to raise awareness of endemic arsenicosis and provide scientific materials for prevention and treatment of the disease.Methods In Xiaxiaoying Village of Yunnan Province,all members of a family with arsenic poisoning patients were investigated in 2013,their health examination and epidemiological survey of arsenic poisoning were carried out,and arsenic poisoning family profiles and personal files were established.Drinking water,hair and urine samples were collected for arsenic content determination,blood samples were collected for biochemical detection,excessively keratose skin was collected for pathological biopsy.Results A total of 33 family members were investigated.Among them 15 were exposed to arsenic and 18 were not exposed to arsenic.Fifteen people exposed to arsenic were found to be have skin lesions,and two eldest males died of skin cancer and cerebral hemorrhage in 1994 and 2009,respectively.The survey found out that 15 patients born in 1935-1983 had been drinking arsenic pesticides polluted well water for 5 to 16 years from 1973 to 1989.As of 2013,the arsenic exposure had been stopped for 24 years,the content of arsenic in the polluted wells was 0.624 mg/L,which was 62.4 times the recommended maximum limit (0.01 mg/L) of the World Health Organization.The median of hair and urinary arsenic in arsenic exposed population and non-arsenic exposed population was 4.2,3.7 mg/kg and 60.9,41.0 μg/L,respectively.There was no statistically significant difference in hair arsenic (Z =-1.905,P ＞ 0.05),but the difference of urinary arsenic was statistically significant (Z =-3.002,P ＜ 0.05).The median of aspartate aminotransferase (AST),gammaglutamyltransferase (γ-GT) and 24 hours urinary ereatinine (Cr) in arsenic exposed population and non-arsenic exposed population was 37.5,31.0 U/L,25.5,12.0 U/L,13 834.0,and 6 843.0 μmol/L,respectively.The differences between the two groups were statistically significant (Z =-2.776,-2.311,-2.502,P ＜ 0.05).Twelve cases of arsenic poisoned patients who were conducted health examination and epidemiological investigation showed typical triad of skin,among them 2 cases were moderate and 10 cases were severe.Pathological biopsy results showed 8 cases had basal cell carcinoma or squamous cell carcinoma.Conclusions Drinking arsenical pesticide contaminated water can induce chronic arsenic poisoning,even after the cessation of arsenic exposure.We should pay close attention to its long-term serious harmful effect.
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Objective To analyze the iodine nutritional status in the key populations before and after the adjustment of iodized salt in Yunnan Province,and to provide scientific basis for adjusting the strategy of prevention and treatment timely.Methods The probability proportional to size sampling method was employed in the investigation.In the pre-adjustment period (2011) and the post-adjustment period (2014),the changes in the residents' iodized salt,the urinary iodine and goiter prevalence of children aged 8-10,the urinary iodine of pregnant women and lactating women were analyzed.Results Before and after adjusting the salt iodine concentration,the coverage rate of iodized salt was 99.1％ (1 196/1 207) and 99.2％ (1 532/1 545),respectively,the mean of salt iodine after the adjustment (23.6 mg/kg) was significantly lower than that of before (30.1 mg/kg,F =17.287,P ＜ 0.01).There was significant difference in the iodine nutritional status of children from 271.4 to 180.9 μg/L (Z=-12.883,P ＜ 0.01).The difference of iodine nutritional status in pregnant women between pre-adjustment (217.3 μg/L) and postadjustment (143.7 μg/L) was also significant (Z =9.997,P ＜ 0.01).The thyroid goiter rate of children had inceased from 1.7％ (21/1 207) to 2.1％ (33/1 549),the difference was not statistically significant between the groups (x2=0.539,P ＞ 0.05).Conclusions After adjusting the salt iodine concentration in Yunnan Province,iodine nutrition of children has decreased from more than adequate level to adequate level,thyroid goiter rate of children has remained at the low level,and iodine nutrition of pregnant women is sightly lower than adequate level,but iodine deficiency of pregnant women is at a low risk because of the good iodized salt coverage.The new standard of iodized salt is appropriate,and it is more favorable to health in Yunnan Province.
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Objectives To study the prevailing status of coal-burning type endemic fluorosis in Fuyuan County of Yunnan Province, and to provide a scientific basis for fluorosis control and prevention. Methods In 2013, five towns were selected from the villages and towns which the defluoridation stove project was implemented and by the end of 2007 defluoridation stove rate was higher than 95%(including 95%), and two natural villages were selected in each township to carry out the investigation. Dental fluorosis was examined of all children aged 8 to 12 of survey points. At least 20 people were selected in each village. At the same time, 20 copies of instant urine samples were collected from these children of half male and half female, and urinary fluoride was determined. Then five natural villages were sampled from all survey points, and permanent residents were divided into25-,35-,45-,55-and≥65groups according to age. Six people were selected from each group with male and female in half who were conducted examination of adult skeletal fluorosis by X-ray. Dental fluorosis diagnosis was based on theDental Fluorosis Diagnosis(WS/T 208-2011). Urinary fluoride determination was done in accordance withUrine-Determination of Fluoride-Ion Specific Electrode Method(WS/T 30-1996). Skeletal fluorosis diagnosis was carried out according to Diagnostic Criteria for Endemic Skeletal Fluorosis (WS 192-2008). Results A total of 556 children aged 8 to 12 were monitored, the detection rate of dental fluorosis was 41.55%(231/556), the dental fluorosis index was 0.78. The very mild, mild, moderate and severe proportions of children's dental fluorosis were 20.50%(114/556), 17.09%(95/556), 3.60%(20/556) and 0.36%(2/556), respectively, given priority to very mild. The prevalence of dental fluorosis in children was increased with increasing age (χ2=74.27, P<0.05). One hundred and ninety-three copies of child urine samples were tested, the geometric mean of urinary fluoride was 0.62 mg/L, and the urinary fluoride contents were between 0.10-2.93 mg/L. A total of 116 adults were examined, and the detection rate of skeletal fluorosis was 9.48%(11/116). Detected cases of skeletal fluorosis was given priority to mild (9 cases, accounted for 81.81%), more men cases [16.36% (9/55)] than those of women [3.28% (2/61), χ2 = 5.77, P< 0.05]. Conclusion The hazard of coal-burning type fluorosis has been reduced in Fuyuan County , the affect of defluoridation stove project is obvious.
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<p><b>OBJECTIVE</b>In order to understand the iodine nutritional status, after the salt-iodine content was showed a reduction in 2012 and to evaluate the current situation after the new standards was brought into force to the general population in an experimental community of Yunnan province.</p><p><b>METHODS</b>Randomly sampled urine and salt were collected, to test the iodine concentration in the study-site. Pre-and post-levels of the iodized salt under the provision of the new standards, were identified.</p><p><b>RESULTS</b>of this study were gathered upon 3 weeks or 3 months, respectively. Results Data from the three randomly chosen study sites showed that the urine iodine concentration in the general populations was reducing gradually. In the general population, medians of Urine Iodine (MUI) were 279.71 µg/L, 239.64 µg/L and 226.26 µg/L, respectively. Proportion of the urine iodine value for 100-199 µg/L increased but ≥300 µg/L decreased, after the new standard was put into practice. Both homogeneity and stability of the new standard on iodized salt seemed to be good.</p><p><b>CONCLUSION</b>Iodine nutrition in general population appeared reasonable under the use of newly set salt-iodine standards in general population living in Yunnan province.</p>