Objective:To investigate the distribution of iodine and other chemical elements in soil, grain and vegetables in different water iodine areas of Xi'an City, and to provide theoretical basis for prevention and treatment of iodine related diseases and water improvement measures.Methods:From September to November 2021, a stratified cluster sampling method was used to select three survey villages in Xi'an, namely Yehu Village, Xingbei Village, and Quanzhong Village, where the iodine level of residents' drinking water < 10, 10 - 100, and > 100 μg/L. Drinking water samples were collected from seven survey sites based on the source of domestic drinking water to determine the iodine level of the water. At the same time, soil samples of cultivated land, residents' grains (wheat, corn), and vegetables were collected from survey villages to determine the content of 14 elements including calcium, iron, magnesium, chromium, nickel, copper, zinc, cadmium, lead, arsenic, mercury, selenium, iodine, and fluoride.Results:The iodine level in the water of 7 survey sites in three survey villages was 5.80, 6.40, 25.51, 42.20, 53.90, 111.65, and 177.63 μg/L, respectively. A total of 70 samples of soil, 65 samples of wheat, 76 samples of corn, and 141 samples of vegetables were collected. Among them, the levels of various elements in vegetables and grains were lower than those in the soil. Only calcium and fluoride were higher in vegetables than in grains, while iron, chromium, copper, zinc, selenium, and iodine were lower in vegetables than in grains. According to the range of water iodine level, there were statistically significant differences in the content of calcium, iron, chromium, nickel, copper, zinc, mercury, iodine, and fluoride in soils from different water iodine regions ( Fcalcium, iron, chromium, nickel = 42.04, 13.55, 12.22, 11.20, Hcopper, zinc, mercury, iodine, fluoride = 14.27, 9.19, 14.72, 25.14, 16.50, P < 0.05). The comparison of magnesium, zinc, cadmium, arsenic, and selenium content in wheat showed statistically significant differences ( Fadmium, selenium = 6.34, 3.31, Hmagnesium, zinc, arsenic = 6.12, 11.55, 6.23, P < 0.05). The comparison of calcium, iron, magnesium, chromium, nickel, copper, zinc, cadmium, lead, arsenic, mercury, iodine, and fluoride content in corn showed statistically significant differences ( Fmagnesium, chromium, nickel, copper, zinc, iodine = 18.89, 13.76, 17.86, 24.17, 28.46, 15.96, Hcalcium, iron, cadmium, lead, arsenic, mercury, fluoride = 11.57, 40.53, 26.50, 33.05, 33.73, 36.01, 29.21, P < 0.05). The comparison of calcium, iron, magnesium, chromium, zinc, cadmium, lead, arsenic, mercury, and selenium content in vegetables showed statistically significant differences ( H = 23.93, 8.12, 10.03, 7.01, 16.09, 18.36, 23.07, 6.51, 27.67, 7.86, P < 0.05). Conclusions:There are significant differences in the distribution of 14 elements in soil, grain, and vegetables in different water iodine regions. In addition to drinking water, precise guidance should also be provided based on the iodine content in soil, grain, and vegetables in different water iodine areas.

Objective:To investigate the distribution of iodine and other chemical elements in soil, grain and vegetables in different water iodine areas of Xi'an City, and to provide theoretical basis for prevention and treatment of iodine related diseases and water improvement measures.Methods:From September to November 2021, a stratified cluster sampling method was used to select three survey villages in Xi'an, namely Yehu Village, Xingbei Village, and Quanzhong Village, where the iodine level of residents' drinking water < 10, 10 - 100, and > 100 μg/L. Drinking water samples were collected from seven survey sites based on the source of domestic drinking water to determine the iodine level of the water. At the same time, soil samples of cultivated land, residents' grains (wheat, corn), and vegetables were collected from survey villages to determine the content of 14 elements including calcium, iron, magnesium, chromium, nickel, copper, zinc, cadmium, lead, arsenic, mercury, selenium, iodine, and fluoride.Results:The iodine level in the water of 7 survey sites in three survey villages was 5.80, 6.40, 25.51, 42.20, 53.90, 111.65, and 177.63 μg/L, respectively. A total of 70 samples of soil, 65 samples of wheat, 76 samples of corn, and 141 samples of vegetables were collected. Among them, the levels of various elements in vegetables and grains were lower than those in the soil. Only calcium and fluoride were higher in vegetables than in grains, while iron, chromium, copper, zinc, selenium, and iodine were lower in vegetables than in grains. According to the range of water iodine level, there were statistically significant differences in the content of calcium, iron, chromium, nickel, copper, zinc, mercury, iodine, and fluoride in soils from different water iodine regions ( Fcalcium, iron, chromium, nickel = 42.04, 13.55, 12.22, 11.20, Hcopper, zinc, mercury, iodine, fluoride = 14.27, 9.19, 14.72, 25.14, 16.50, P < 0.05). The comparison of magnesium, zinc, cadmium, arsenic, and selenium content in wheat showed statistically significant differences ( Fadmium, selenium = 6.34, 3.31, Hmagnesium, zinc, arsenic = 6.12, 11.55, 6.23, P < 0.05). The comparison of calcium, iron, magnesium, chromium, nickel, copper, zinc, cadmium, lead, arsenic, mercury, iodine, and fluoride content in corn showed statistically significant differences ( Fmagnesium, chromium, nickel, copper, zinc, iodine = 18.89, 13.76, 17.86, 24.17, 28.46, 15.96, Hcalcium, iron, cadmium, lead, arsenic, mercury, fluoride = 11.57, 40.53, 26.50, 33.05, 33.73, 36.01, 29.21, P < 0.05). The comparison of calcium, iron, magnesium, chromium, zinc, cadmium, lead, arsenic, mercury, and selenium content in vegetables showed statistically significant differences ( H = 23.93, 8.12, 10.03, 7.01, 16.09, 18.36, 23.07, 6.51, 27.67, 7.86, P < 0.05). Conclusions:There are significant differences in the distribution of 14 elements in soil, grain, and vegetables in different water iodine regions. In addition to drinking water, precise guidance should also be provided based on the iodine content in soil, grain, and vegetables in different water iodine areas.

Objective:To explore the impact of whole blood organophosphate esters (OPEs) flame retardant exposure on thyroid function-related hormones in healthy older adults.Methods:In this panel study, five repeated population-based epidemiological surveys and biological sample collection were conducted from September 2018 to January 2019, with 76 healthy older adults aged 60-69 years in the Dianliu Community of Jinan, Shandong Province. Information on the sociodemographic characteristics, diet, and health status of the respondents was systematically gathered through questionnaires and physical examinations. Fasting venous blood was collected to determine the levels of OPEs, thyroid-stimulating hormone (TSH), triiodothyronine (T 3), and thyroxine (T 4). A linear mixed-effects model was used to analyze the impact of OPEs exposure on thyroid function-related hormones in healthy older adults. Results:Each of the 76 subjects participated in at least two follow-up visits, resulting in a total of 350 person visits. The age of the study participants was (65.07±2.76) years, with 38 participants of both sexes. A total of eight OPEs were included with a detection rate exceeding 50%, and the M ( Q 1, Q3) for ∑OPEs was 3.85 (2.33, 5.74) ng/ml, with alkyl-OPEs being the major type of OPEs with an M ( Q 1, Q3) of 1.27 (0.64, 2.50) ng/ml. The M ( Q 1, Q3) for TSH, T 3, and T 4 was 3.74 (2.55, 5.69) μIU/ml, 1.32 (1.10, 1.60) ng/ml, and 45.04 (36.96, 53.27) ng/ml, respectively. Linear mixed-effects model showed that TSH was significantly decreased by 9.93% (95% CI:-15.17%, -4.36%) and 11.14% (95% CI:-15.94%, -6.06%) in older adults for each quartile level increase in TnBP and TEHP exposures, respectively. Gender-stratified analysis indicated that TEHP exposure was negatively associated with TSH levels in male older adults, whereas a decrease in TSH levels among female older adults was associated with TnBP exposure. Conclusion:Exposure to whole blood OPEs is associated with decreased TSH levels among healthy older adults, with notable gender differences.

Objective:To explore the impact of whole blood organophosphate esters (OPEs) flame retardant exposure on thyroid function-related hormones in healthy older adults.Methods:In this panel study, five repeated population-based epidemiological surveys and biological sample collection were conducted from September 2018 to January 2019, with 76 healthy older adults aged 60-69 years in the Dianliu Community of Jinan, Shandong Province. Information on the sociodemographic characteristics, diet, and health status of the respondents was systematically gathered through questionnaires and physical examinations. Fasting venous blood was collected to determine the levels of OPEs, thyroid-stimulating hormone (TSH), triiodothyronine (T 3), and thyroxine (T 4). A linear mixed-effects model was used to analyze the impact of OPEs exposure on thyroid function-related hormones in healthy older adults. Results:Each of the 76 subjects participated in at least two follow-up visits, resulting in a total of 350 person visits. The age of the study participants was (65.07±2.76) years, with 38 participants of both sexes. A total of eight OPEs were included with a detection rate exceeding 50%, and the M ( Q 1, Q3) for ∑OPEs was 3.85 (2.33, 5.74) ng/ml, with alkyl-OPEs being the major type of OPEs with an M ( Q 1, Q3) of 1.27 (0.64, 2.50) ng/ml. The M ( Q 1, Q3) for TSH, T 3, and T 4 was 3.74 (2.55, 5.69) μIU/ml, 1.32 (1.10, 1.60) ng/ml, and 45.04 (36.96, 53.27) ng/ml, respectively. Linear mixed-effects model showed that TSH was significantly decreased by 9.93% (95% CI:-15.17%, -4.36%) and 11.14% (95% CI:-15.94%, -6.06%) in older adults for each quartile level increase in TnBP and TEHP exposures, respectively. Gender-stratified analysis indicated that TEHP exposure was negatively associated with TSH levels in male older adults, whereas a decrease in TSH levels among female older adults was associated with TnBP exposure. Conclusion:Exposure to whole blood OPEs is associated with decreased TSH levels among healthy older adults, with notable gender differences.

Objective:To investigate the impact of a reduced portacaval shunt on hepatic myelopathy (HM) in patients with cirrhosis after a transjugular intrahepatic portosystemic shunt (TIPS).Methods:Patients who developed HM after receiving TIPS at the First Affiliated Hospital of Xi'an Jiaotong University from January 2013 to June 2018 were retrospectively analyzed. HM severity was quantified by clinical spasticity index (CSI) and Fugl-Meyer Assessment (FMA) of the lower extremity. Clinical manifestations were combined with grades Ⅰ-Ⅳ. HM patients were divided into drug treatment (group A) and flow restriction group (group B) according to different treatment methods. The changes in CSI and FMA of the lower extremity after treatment were statistically analyzed in the two groups. P<0.05 was considered a statistically significant difference. Results:A total of 421 cases of cirrhosis who underwent TIPS were enrolled. Among them, 30 developed HM, with 22 in group A and 8 in group B. The incidence of HM after TIPS surgery was about 7.13%. After treatment, CSI was gradually increased and FMA of lower extremity was gradually decreased in group A, while vice-versa in group B. CSI in the two groups were differed significantly at 6, 12, 18, and 24 months after treatment ( P<0.05), while the difference in FMA of the lower extremity was statistically significant at 12, 18, and 24 months after treatment ( P<0.05). CSI was decreased and FMA of lower extremity was increased after treatment in patients with group A HM grade I. CSI, and FMA of lower extremity changes were statistically significant ( P<0.05) when compared with patients with HM grades Ⅱ-Ⅳ. The incidence of hepatic encephalopathy was significantly lower in group B than that in group A ( P=0.034), but there was no statistically significant difference between the two groups in the incidence of gastrointestinal bleeding, ascites, infection, MELD score and mortality. Conclusion:A reduced portacaval shunt can improve HM in patients with liver cirrhosis after TIPS, and drug therapy alone is effective for patients with early HM grade I.

Objective: To evaluate the dynamic prevalence of dental fluorosis of children and levels of fluoride in drinking water after improvement of water in Xi an City, to provide scientific basis for water fluoridation improvement. Methods: A total of 35 fluorosis endemic villages were selected as fixed monitor sites in 2014-2018, the ways of water improvement were surveyed, water fluorine content were detected and the prevalence of dental fluorosis in children aged 8 to 12 years were examined. Results: Rates of excess fluoride in drinking water from 2014 to 2018 were 22.86%, 14.29%,11.43%, 11.43% and 8.57%, the difference were significant(χ2=16.44, P<0.01).The dental fluorosis detection rates of children aged 8 to 12 years were 20.89%,18.22%,17.46%,18.13% and 16.76% in 2014-2018 which showed a obvious descending trend by year(χ2=10.02, P<0.01). The detection rate of dental fluorosis in children aged 8 and 9 years showed a decreasing trend by year(χ2=6.53, 4.54, P<0.05).The difference of total rate of dental fluorisis,rate of mild cases rate of moderate-to-severe cases were statistically between the villages without qualified water and the villages with normal fluorine water(χ2=179.22, 167.93,10.35, P<0.01). The rate of detection in the villages with the water fluorine exceed standard in 2014-2018 showed a declining trend year by year(χ2=28.50, P<0.01). The detection rate were significant different across water improvement methods(χ2=197.76, P<0.01). Detection rate of dental fluorosis decreased from 2014 to 2018 in the areas with municipal water supply showed a decreasing after year(χ2=12.16, P<0.01). Conclusion The improvement of municipal water supply shows significant effects on water fluorosis control, the detection rate of water fluoride and children s dental fluorosis in some villages with the other ways of water improvement are still higher than expected, the continuously monitor of fluoride content in water and dental fluorosis in children should be strengthened.

Objective:To evaluate the effect of different water-improving methods on dental fluorosis of children aged 8 to 12 in drinking-water-borne fluorosis areas in Xi'an City, and provide basis for making fine prevention and control measures.Methods:In 2018, 50 drinking-water-borne fluorosis villages in Xi'an City with water improvement time from 2011 to 2013 were selected as survey sites. The condition and the way of water improvement were surveyed, water fluoride content was determined and the prevalence of dental fluorosis in children aged 8 to 12 was examined, and the rates of dental fluorosis were compared before and after the water improvement in the 50 villages.Results:The water-improving projects were in normal operation in 50 villages. The medians of water fluoride content were 0.31, 0.88 and 1.14 mg/L in villages with municipal water supply, low fluorine well and defluoridation treatment water supply (the villages of different water-improvement methods were 12, 24 and 14, respectively), the differences were statistically significant ( H = 75.54, P < 0.01). The qualification rates of water fluoride in villages with different water-improvement methods were 100.00% (12/12), 79.17% (19/24) and 57.14% (8/14), and the difference was statistically significant (χ 2 = 6.95, P < 0.05). The detection rate of dental fluorosis was 43.17% (218/505) in the 11 villages with excessive water fluoride content, and the detection rate was 20.77% (331/1 594) in the 39 villages with qualified water fluoride content, the difference was statistically significant (χ 2 = 99.66, P < 0.01). After water improvement, the total detection rate of dental fluorosis (26.16%, 549/2 099) in the 50 villages was lower than that before water improvement (41.66%, 959/2 302), the difference was statistically significant (χ 2 = 117.17, P < 0.01). The detection rates of dental fluorosis were reduced after the water improvement in villages with municipal water supply and low fluorine well, the differences were statistically significant (χ 2 = 74.37, 69.36, P < 0.01). The detection rate was declined after water improvement in villages with defluoridation treatment water supply, but the difference was not significant (χ 2 = 0.78, P > 0.05). There was a statistically significant difference in the detection rate of dental fluorosis among children in villages with different water-improvement methods (χ 2 = 72.79, P < 0.01). The detection rate of dental fluorosis in villages with defluoridation treatment water supply [39.53% (200/506)] was higher than that in villages with municipal water supply [17.97% (133/740)] and low fluorine well [25.32% (216/853)], the differences were statistically significant ( P < 0.017); the detection rate of dental fluorosis in villages with municipal water supply was lower than that in villages with low fluorine well ( P < 0.017). Conclusions:The dental fluorosis of children's has been effectively controlled in the villages after water improvement in Xi'an City. The fluoride content in the water and the detection rate of dental fluorosis in children in some endemic areas are still high. It is necessary to further improve the water quality or consolidate the improvement effect as soon as possible.

Objective:To assess the implementation of control measures and dental fluorosis of children in drinking-water-borne endemic fluorosis areas in Xi'an City, and to evaluate the implementation effects of the prevention and control measures.Methods:All drinking-water-borne endemic fluorosis villages in Xi'an were selected as the investigation sites. The progress and running condition of all water-improved projects were investigated, fluoride concentration in all the water-improved projects and tap water were tested. "Standard Test Method for Drinking Water" (GB/T 5750.5-2006) was used to test the water fluoride. A cross-sectional analytical study was conducted on school children aged 8 - 12 years old, the dental fluorosis was determined according to "Diagnosis of Dental Fluorosis" (WS/T 208-2011).Results:There were 273 drinking-water-borne endemic fluorosis villages, the rate of water improved villages was 91.58% (250/273), and all of the water-improved projects were operating normally (100.00%, 196/196). The rate of water-improved projects with qualified water fluoride was 88.27% (173/196), 237 villages had fluoride safe drinking water and the qualified rate was 86.81% (237/273). The median of water fluoride in the 250 villages with water-improved projects was 0.78 mg/L, the median was 0.83 mg/L in the 23 villages without water-improved projects, and the difference was not significant ( Z = 1.475, P > 0.05) . The overall prevalence of dental fluorosis among children aged 8 - 12 years old was 19.86% (1 960/9 871), and the dental fluorosis index was 0.39. The prevalence of dental fluorosis in the villages with qualified water fluoride was 16.13% (1 377/8 539), and the rate was 43.77% (583/1 332) in the villages with unqualified water fluoride, and the difference was significant (χ 2 = 553.283, P < 0.01). The prevalence of dental fluorosis in children with water fluoride content of 0.00 - 1.20, 1.21 - 1.50, and ≥1.51 mg/L was 16.13% (1 377/8 539), 41.20% (281/682), 46.46% (302/650), and the difference was significant (χ 2 = 559.011, P < 0.01), the severity of the disease was positively correlated with water fluorine concentration ( r = 0.273, P < 0.01). The epidemic situation in 202 villages was effectively controlled and 71 villages did not reach the control standard. Conclusions:The progress of water-improved projects and the rate of qualified water fluoride are not optimistic in Xi'an, the dental fluorosis of children is still higher than the government standard in the high fluoride drinking-water areas. The measures for water improving defluorination and disease surveillance should be strengthened.

Objective To assess the effects of defluoridation on prevalence of children's dental fluorosis in Xi'an City and study related influencing factors.Methods In 2017,the survey results of 2013 were collected from the previous investigation of drinking water type fluorosis in Xi'an Center for Disease Control and Prevention,and villages from drinking water type fluorosis areas were divided into five groups:0.0-,0.2-,0.5-,1.0-,and ≥ 1.5 mg/L,according to the fluoride concentrations of water.Four villages were randomly selected from each group,a total of 20 villages were selected as the investigation sites.A cross-sectional analytical study was conducted in the 20 villages,the fluoride in drinking water,the dental fluorosis of children aged 8-12 years and fluoride content in urine were detected,and the survey results were compared with those of 2013.Children were divided into five groups according to urinary fluoride contents as:0.0-(control),0.4-,0.8-,1.2-,and ≥ 1.6 mg/L,and the logistic regression model was used to evaluate the risk of dental fluorosis.Results There were no significant differences in water fluoride content between 2013 and 2017 (P ＞ 0.05).The rates of dental fluorosis among the study population in 2013 and 2017 were 25.35％ (200/789) and 20.58％ (164/797),and the difference was significant (x2 =5.11,P＜0.05).The prevalence rate and severity of dental fluorosis in 2013 [3.52％ (9/256),13.28％ (17/128),31.62％ (43/136),37.82％(45/119),57.33％(86/150)] and 2017[4.02％(10/249),11.82％(13/110),18.05％(24/133),29.13％(37/127),44.94％ (80/178)] were significantly increased with increase of water fluoride concentration (x2 =168.02,117.83,P ＜ 0.01).The prevalence rate of dental fluorosis was higher than 30％ in the three groups with water fluoride content 0.5-,1.0-and ≥ 1.5 mg/L in 2013,and the prevalence rates were decreased in these groups in 2017.The prevalence rate of dental fluorosis was lower than 30％ in the groups with water-fluorine content of 0.5-,1.0-＜1.5 mg/L,while the rate of dental fluorosis in the group with water-fluorine content of higher than 1.5 mg/L was still over 40％.The geometric mean of urinary fluoride of children in 2013 and 2017 were 1.02,0.67 rg/L,and the difference was significant (t =10.24,P ＜ 0.01).There were significant differences in children urinary fluoride between water fluoride groups in 2013 and 2017 (F =85.36,151.14,P ＜ 0.01).The risk of dental fluorosis increased with increase of urinary fluoride content,the odds ratio (OR) values were 5.26,7.83 and 13.28 in the three groups with the urinary fluoride 0.8-,1.2-,≥1.6 mg/L in 2013;the OR values in 2017 were 5.18,7.65 and 13.36,the differences were statistically significant (P ＜ 0.05).Conclusions The situation of water fluoride and dental fluorosis are not optimistic after defluoridation of drinking water.It is necessary to reinforce the measures of water defluoridation,and carry out classified management in endemic fluorosis areas.

Objective To investigate the dental fluorosis and intelligence level of children in drinking water-type of endemic fluorosis areas in Xi'an,and to provide a scientific basis for development of prevention and control strategies.Methods In 2016,six drinking water-type of endemic fluorosis villages and one non-diseased village were selected as investigation sites in Xi'an.According to the detection rate and prevalence of dental fluorosis in children,six diseased villages were divided into three groups,the disease light-affected areas were Huidong and Xingnan,the moderate-affected areas were Liulin and Xiazhu,and the serious-affected areas were Hetou and Xiaoyang;and the Deng village was the non-diseased.A cross-sectional survey was conducted to collect 3 tap water samples in each village to test the fluorine content in water.For all children aged 8 to 12 years in diseased villages and 100 children aged 8 to 12 years in non-diseased villages,dental fluorosis examination and intelligence test were carried out.Results Mean value of water fluoride in non-diseased village and endemic fluorosis areas were (0.25 ± 0.01),(0.78 ± 0.43) mg/L,and the water fluoride content in two diseased villages was over 1.20 mg/L.The detection rate of dental fluorosis in children aged 8 to 12 (30.32％,67/221) in diseased areas was significantly higher than that in non-diseased area (2.00％,2/100;x2 =31.32,P ＜ 0.01).Children's IQ scores in the four groups were 108.68 ± 10.83,102.54 ± 12.54,101.70 ± 14.85,93.45 ± 10.84,and the IQ scores were decreased with the severity of dental fluorosis,the difference in IQ scores was significant between the endemic fluorosis areas and non-endemic fluorosis area (P ＜ 0.05);the percentage of children with IQ≤89 in endemic fluorosis areas was significantly higher than that in non-endemic fluorosis area (x2 =22.02,P ＜ 0.01).The IQ scores of children with dental fluorosis was 94.96 ± 13.75,and the IQ was 105.26 ± 10.19 in children with normal condition,the difference was significant (t =5.61,P ＜ 0.01),the mean value of IQ was decreased with the severity of dental fluorosis (F =7.42,P ＜ 0.05),the percentage of children with IQ≤89 in patient was higher than that in normal children,the difference was significant (x2 =45.70,P ＜ 0.01).Conclusion Low level of water fluoride still has negative influence on children's dental health and intelligence,water improving and surveillance should be strengthened to ensure the health of children.