1.Monitoring and analysis of arsenic pollution in Yangzonghai lake and the influence of arsenic to the surrounding drinking water and local food in Chengjiang of Yunnan province in 2008 and 2009
Bang-hui, SHI ; Jian-quan, WANG ; Hong, LI ; Yong-fu, MA ; Li-hong, LIANG ; Long, YANG ; Chong-yi, MA ; Yun-hua, KANG ; Xue-ying, XU ; Rong, XU ; Yan-jiao, XU ; Yan-hong, LI
Chinese Journal of Endemiology 2011;30(1):47-50
Objective To find out the arsenic pollution in Yangzonghai lake and its influence to the surrounding drinking water source and the local food and to provide a scientific basis for arsenic pollution control,drinking water and food safety. Methods Arsenic monitoring were carried out in 10 points of Yangzonghai lake,45 water sources within 5 km of Yangzonghai lake, and locally produced food. Results From September 2008 to December 2009, the water arsenic concentrations of Yangzonghai lake ranged 0.06 - 0.18 mg/L, the average arsenic concentrations were 0.12 mg/L and 0.10 mg/L for 2008 and 2009, respectively, the value of 2009 was higher, and the difference was statistically significant(t = 3.284, P < 0.05). There were no significant difference in the average of arsenic concentration of Yangzonghai lake between the dry and rainy season in 2009(t = 0.905, P >0.05). The arsenic concentrations from the No. 3 spring water ranged from 0.12 - 30.36 mg/L. After a peak value early in October 2008, the No. 3 spring water showed a downward trend month by month. In 2008 the average arsenic concentration was 23.92 mg/L, 2009 was 2.41 mg/L, down 89.92% over the previous year, the difference was statistically significant(t = 9.582, P < 0.05 ). In January and February 2009, the average arsenic concentration (11.96 mg/L) was significantly higher than those of March-December(0.50 mg/L, t = 57.759, P< 0.05). In Yangzong town, the arsenic concentration in the drinking water and river met the national drinking water health standards. Among 78 samples monitored of the locally produced food in Yangzong town, 77 passed, with a pass rate of 98.72%. Conclusions Arsenic contamination has been effectively controlled. The drinking water and local food production has not been contaminated by arsenic except aquatic products in Yangzonghai Lake. It is recommended to take effective measures to prevent water contamination.
2.Relationship Between ABO Blood Group and Acute Non-ST-segment Elevation Myocardial Infarction Occurrence
fei Hong JIAO ; cheng Jian LIANG ; Quan LI ; guo Bang YANG ; peng Xian YU ; ling Xiao ZHANG ; yun Jia ZHANG ; zhi Xue SUN ; le Huan WANG ; Chao XU
Chinese Circulation Journal 2017;32(10):981-983
Objective: To explore the relationship between ABO blood group and acute non-ST-segment elevation myocardial infarction (NSTEMI) occurrence. Methods: Our research included 2 groups: NSTEMI group, 1039 relevant patients treated in Anzhen hospital from 2013-01 to 2014-12 were retrospectively enrolled; Control group, 1039 subjects with normal coronary artery which was confirmed by coronary angiography. The Baseline condition including age, previous disease history and ABO blood group was studied. Logistic regression model was used to conduct single and multivariate analysis. Results: In NSTEMI group and Control group, blood type A was 287/1039 (27.6%) vs 259 (24.9%), type B was 345 (33.3%) vs 356 (34.3%), type AB was 102 (9.8%) vs 114 (11.0%) and type O was 305 (29.4%) vs 310 (29.8%), ABO blood group distribution for A and non-A, B and non-B, AB and non-AB blood group, O and non-O had no statistic meaning between 2 groups, P>0.05. Logistic regression analysis indicated that with adjusted risk factors of MI such as age, gender, hypertension, diabetes, hyperlipemia, cerebrovascular disease and smoking, the patients with blood types A, B and AB had the similar risk for NSTEMI occurrence than type O patients; there was no relationship between ABO blood group and NSTEMI occurrence. Conclusion: ABO blood group had no relationship to NSTEMI occurrence.