Identification and risk monitoring of potential risk areas of schistosomiasis in Dongting Lake area
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摘要:
目的 识别和监测洞庭湖地区血吸虫病潜在风险区。 方法 借助遥感技术(remote sensing,RS)和地理信息系统(geographic information system,GIS)技术,利用光谱特征和环境因子特征,提取洞庭湖地区血吸虫病潜在风险区。基于流行病学数据和土地利用数据测算地区疫情指数和环境易感指数,与潜在疫情风险区在洞庭湖区格网系统中融合,形成2006-2016年洞庭湖区血吸虫病流行风险监测图。 结果 2006-2016年洞庭湖地区血吸虫疫情高风险区集中在常德市辖区中、北部临湖地区(年平均疫情指数R=0.330 5,区域平均易感指数Y=2.458 2),敏感地类为湖泊地区(敏感度系数β=1.236 6),南县及沅江市北部大通湖周边地区(R=0.426 0,Y=0.836 8),敏感地类为水田地区(β=0.202 1)和其他建设用地(β=0.308 0)。极高风险区集中在津市境内部分临湖地区(R=0.449 1,R=3.917 0),敏感地类为有林地(β=1.234 5)。流域风险从高到低依次为澧水、沅水、资水、湘江。 结论 洞庭湖地区要将高风险、极高风险地区作为未来疫情控制的重点,并做好疏林地、高覆盖度草地、水库坑塘等疫情敏感地类的查灭螺和环境整治工作。 Abstract:Objective To identify and monitor potential risk areas of schistosomiasis in Dongting Lake area. Methods With remote sensing (RS)and geographic information system(GIS) technology, potential risk areas of schistosomiasis in Dongting Lake area were extracted by using spectral characteristics and environmental factors. Based on epidemiological data and land use data, the regional epidemic index and environmental susceptibility index were fused with potential epidemic risk areas in the grid system of Dongting Lake area to form the epidemic risk surveillance map of schistosomiasis in Dongting Lake area from 2006 to 2016. Results From 2006 to 2016, the high risk areas of schistosomiasis epidemic in Dongting Lake area were concentrated in the central and Northern lakeside areas of Changde City (Annual average epidemic index R=0.330 5, Regional average susceptibility index Y=2.458 2), the sensitive land types were Lake area (Sensitivity coefficient β=1.236 6), the surrounding area of Datong Lake in Nanxian and Northern Yuanjiang City (R=0.426 0, Y=0.836 8), paddy field area (β=0.202 1) and other construction land (β=0.308 0). The extremely high risk areas were concentrated in some lake-facing areas in Jinshi (R=0.449 1, Y=3.917 0) and the sensitive land type is woodland(β=1.234 5). The risk of river basin from high to low was respectively the Lishui River, the Yuanjiang River, the Zijiang River and the Xiangjiang River. Conclusions The high-risk and extremely high-risk areas should be the focus of future epidemic control. The snail control and environmental renovation of epidemic-sensitive areas such as sparse woodland, grassland with high coverage, reservoir pits and ponds should be done well in Dongting Lake area. -
Key words:
- Schistosomiasis /
- Potential risk areas /
- Monitoring
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表 1 洞庭湖地区血吸虫病潜在风险区疫情指数R
Table 1. Epidemic index of potential risk areas of schistosomiasis in Dongting Lake area
地区 2006年 2008年 2010年 2012年 2014年 2016年 平均值 汉寿县 0.084 6 0.083 1 0.087 0 0.084 6 0.080 6 0.079 1 0.083 2 安乡县 0.322 2 0.294 2 0.343 2 0.491 0 0.436 3 0.408 9 0.382 6 澧县 0.297 6 0.303 8 0.282 9 0.214 1 0.187 2 0.254 3 0.256 7 津市市 0.545 8 0.467 1 0.223 3 0.536 6 0.437 1 0.484 7 0.449 1 临澧县 0.025 0 0.069 9 0.060 6 0.074 5 0.074 1 0.041 9 0.057 7 常德市辖区 0.271 9 0.287 3 0.345 0 0.388 0 0.384 0 0.306 6 0.330 5 岳阳县 0.087 7 0.077 1 0.122 4 0.148 1 0.150 5 0.140 1 0.121 0 湘阴县 0.071 5 0.109 7 0.074 4 0.085 1 0.057 8 0.054 9 0.075 6 华容县 0.235 4 0.189 6 0.141 6 0.165 8 0.226 5 0.247 0 0.201 0 汨罗市 0.060 5 0.072 6 0.048 9 0.080 3 0.092 7 0.192 6 0.091 3 临湘市 0.043 9 0.056 0 0.047 3 0.046 1 0.039 4 0.046 8 0.046 6 岳阳市辖区 0.190 6 0.202 2 0.258 5 0.400 6 0.280 6 0.339 3 0.278 6 沅江市 0.231 2 0.377 6 0.261 1 0.223 5 0.339 4 0.275 3 0.284 7 南县 0.261 7 0.385 3 0.238 9 0.270 9 0.316 6 0.546 6 0.336 7 益阳市辖区 0.228 1 0.262 3 0.333 6 0.333 4 0.276 1 0.281 6 0.285 9 表 2 部分流行疫区9个土地利用类型的疫情敏感度系数β
Table 2. Sensitivity coefficient of 9 land use types in epidemic areas
地类编号 津市市 南县 沅江市 华容县 澧县 常德市辖区 岳阳市辖区 益阳市辖区 11 -0.140 2a 0.202 1b 0.039 5b -0.106 2b 0.022 6a 0.010 7 0.087 4b -0.034 5b 21 2.470 9 -0.178 9 0.023 9b 0.043 8b 0.041 0a -1.524 9a -0.106 0b -0.377 1a 23 2.064 8a -0.289 2b -0.048 9b -0.130 8b -0.029 2 2.075 7a -0.259 2b 0.126 9a 31 0.002 7 -0.165 2c 0.085 6 0.052 2b 0.307 2b -0.039 0 0.113 5b 0.115 8 42 0.009 4c -0.047 1b 0.027 5a -0.003 1b 0.082 2a 1.236 6a -0.033 6b 0.123 8a 43 1.395 3b -0.047 3b 0.124 5a 0.035 3b -0.037 2c -0.139 1c -0.137 6 -0.461 7a 52 -0.757 8a 0.074 6b -0.088 5b -0.108 8b 0.182 4a 0.316 0 -0.124 2b 0.427 8 53 -2.341 3b 0.004 9b 0.308 0c 0.664 2b -0.022 1b 0.546 7a 0.161 4b 0.288 2a 64 0.036 3c 0.047 2b -0.022 0b -0.147 7b -0.251 8c 0.061 3 -0.030 6b -0.020 6b 注:a表示该系数值在95%置信水平下有统计学意义;b表示该系数值在99%置信水平下有统计学意义;c表示该系数值在90%置信水平下有统计学意义。 -
[1] 胡本骄, 赵正元, 夏蒙, 等. 2004-2011年湖南省居民血吸虫感染时空特征研究[J]. 中国血吸虫病防治杂志, 2017, 29(4): 406-411. DOI: 10.16250/j.32.1374.2016127.Hu BJ, Zhao ZY, Xia M, et al. Studies on spatial and temporal characteristics of schistosomiasis infection in Hunan residents from 2004 to 2011[J]. Chin J Schi Contl, 2017, 29(4): 406-411. DOI: 10.16250/j.32.1374.2016127. [2] De Souza Gomes EC, LealNeto OB, Albuquerque J, et al. Schistosomiasis transmission and environmental change: a spatio-temporal analysis in Porto de Galinhas, Pernambuco-Brazil[J]. Int J Health Geogr, 2012, 11: 51. DOI: 10.1186/1476-072X-11-51. [3] 薛建, 程晓松, 林荣, 等. 基于地理信息系统的烟台市艾滋病疫情聚集性空间分布[J]. 中华疾病控制杂志, 2018, 22(12): 1216-1220, 1314. DOI: 10.16462/j.cnki.zhjbkz.2018.12.004.Xue J, Cheng XS, Lin R, et al. Spatial distribution of AIDS epidemic in Yantai City based on Geographic Information System[J]. Chin J Dis Control Prev, 2018, 22(12): 1216-1220, 1314. DOI: 10.16462/j.cnki.zhjbkz.2018.12.004. [4] 谢谦, 朱翔, 贺清云. 基于人水相互作用机理的洞庭湖区血吸虫病感染风险研究[J]. 中华疾病控制杂志, 2017, 21(1): 61-64, 76. DOI: 10.16462/j.cnki.zhjbkz.2017.01.014.Xie Q, Zhu X, He QY. Risk study of schistosomiasis infection in Dongting Lake area based on human-water interaction mechanism[J]. Chin J Dis Control Prev, 2017, 21(1): 61-64, 76. DOI: 10.16462/j.cnki.zhjbkz.2017.01.014. [5] 许骏, 贺清云, 蔡建新, 等. 基于熵值灰色关联度模型的血防措施研究[J]. 现代预防医学, 2015, 42(12): 211-2115, 2120. https://www.cnki.com.cn/Article/CJFDTOTAL-XDYF201512001.htmXu J, He QY, Cai JX, et al. Study on schistosomiasis control measures based on entropy grey relational degree model[J]. Modern Preventive Medicine, 2015, 42(12): 211-2115, 2120. https://www.cnki.com.cn/Article/CJFDTOTAL-XDYF201512001.htm [6] 操治国, 汪天平, 张世清, 等. 2008年安徽省血吸虫病潜在流行区疫情监测预警报告[J]. 中国病原生物学杂志, 2010, (3): 195-197, 209. DOI: 10.13350/j.cjpb.2010.03.023.Cao ZG, Wang TP, Zhang SQ, et al. Report on surveillance and early warning of schistosomiasis in potential endemic areas of Anhui Province in 2008[J]. Journal of Pathogen Biology, 2010, (3): 195-197, 209. DOI: 10.13350/j.cjpb.2010.03.023. [7] 秦建新, 仇应山. 洞庭湖区钉螺与血吸虫人畜感染的空间回归分析[J]. 中国热带医学, 2013, 13(9): 1071-1073. DOI: 10.13604/j.cnki.46-1064/r.2013.09.011.Qin JX, Qiu YS. Spatial regression analysis of oncomelania hupensis and schistosomiasis infection in Dongting Lake area[J]. China Tropical Medicine, 2013, 13(9): 1071-1073. DOI: 10.13604/j.cnki.46-1064/r.2013.09.011. [8] 段增强, P.H. Verburg, 张凤荣, 等. 土地利用动态模拟模型的构建及其应用——以北京市海淀区为例[J]. 地理学报, 2004(6): 1037-1047. https://www.cnki.com.cn/Article/CJFDTOTAL-DLXB200406027.htmDuan ZQ, P.H. Verburg, Zhang FR, et al. Construction and application of land use dynamic simulation model-Take Haidian District of Beijing as an example[J]. ACTA GEOGRAPHICA SINICA, 2004(6): 1037-1047. https://www.cnki.com.cn/Article/CJFDTOTAL-DLXB200406027.htm [9] 朱政, 贺清云, 孙泽民. 岳阳市洞庭湖区洲滩地貌类型与钉螺密度的空间相关性分析[J]. 中华疾病控制杂志, 2016, 20(11): 1127-1130, 1150. DOI: 10.16462/j.cnki.zhjbkz.2016.11.013.Zhu Z, He QY, Sun ZM. Spatial correlation analysis between landform types and snail density of beaches in Dongting Lake area of Yueyang City[J]. Chin J Dis Control Prev, 2016, 20(11): 1127-1130, 1150. DOI: 10.16462/j.cnki.zhjbkz.2016.11.013. [10] Guimar es RJ, Freitas CC, Dutra LV, et al. Schistosomiasis risk estimation in Minas Gerais State, Brazil, using enviornmental data and GIS techniques[J]. Acta Tropica, 2008, 108: 234-241. DOI: 10.1016/j.actatropica.2008.07.001. [11] Fonseca F, Freitas C, Dutra L, et al. Spatial modeling of the schistosomiasis mansoni in Minas Gerais State[J]. Acta Tropica, 2014, 5(133): 56-63. DOI: 10.1016/j.actatropica.2014.01.015. [12] 周晓农, 姜庆五, 郭家钢, 等. 我国血吸虫病传播阻断实现路径的探讨[J]. 中国血吸虫病防治杂志, 2012, 24(1): 1-4. DOI: 10.16250/j.32.1374.2012.01.024.Zhou XL, Jiang QW, Guo JG, et al. Discussion on the realization path of schistosomiasis transmission interruption in China[J]. Chin J Schi Contl, 2012, 24(1): 1-4. DOI: 10.16250/j.32.1374.2012.01.024. [13] 薛靖波, 张利娟, 王强, 等. 高分辨率遥感技术在日本血吸虫病监测中的应用[J]. 中国血吸虫病防治杂志, 2015, 27(5): 551-554. DOI: 10.16250/j.32.1374.2015072.Xue JB, Zhang LJ, Wang Q, et al. Application of high resolution remote-sensing technology in the surveillance of schistosomiasis japonica[J]. Chin J Schi Contl, 2015, 27(5): 551-554. DOI: 10.16250/j.32.1374.2015072. [14] Schur N, Kabatereine N, Kristensen T, et al. Spatially explicit schistosoma infection risk in eastern Africa using Bayesian geostatistical modelling[J]. Acta Tropica, 2013, 128(2): 365-377. DOI: 10.1016/j.actatropica.2011.10.006. [15] 黄菊梅, 刘可群, 常艾, 等. 洞庭湖区血吸虫的中间宿主——钉螺对气象因子的响应[J]. 公共卫生与预防医学, 2015, 26(2): 27-30. https://www.cnki.com.cn/Article/CJFDTOTAL-FBYF201502008.htmHuang JM, Liu KQ, Chang A, et al. Intermediate host of schistosomiasis in Dongting Lake area-Response of Oncomelania hupensis to meteorological factors[J]. J of Pub Health and Prev Med, 2015, 26(2): 27-30. https://www.cnki.com.cn/Article/CJFDTOTAL-FBYF201502008.htm [16] Steinmann P, Keiser J, Bos R, et al. Schistosomiasis and water resources development: systematic review, meta-analysis, and estimates of people at risk[J]. Lancet Infectious Diseases, 2006, 6(7), 411-425. DOI: 10.1016/S1473-3099(06)70521-7.