Li Y L, Dang H, Guo S Y, Cao C L, Lü S, Xu J, Li S Z
National Institute of Parasitic Diseases, Chinese Center for Disease Control and Prevention (Chinese Center for Tropical Diseases Research); NHC Key Laboratory of Parasite and Vector Biology; WHO Collaborating Centre for Tropical Diseases; National Center for International Research on Tropical Diseases, Shanghai 200025, China.
Zhongguo Xue Xi Chong Bing Fang Zhi Za Zhi. 2021 Apr 20;33(2):127-132. doi: 10.16250/j.32.1374.2020349.
To analyze the monitoring data of s in the national schistosomiasis surveillance sites of China from 2015 to 2019, so as to understand the changes of snail status in the schistosomiasis-endemic areas of China and to provide the scientific evidence for snail control.
According to the requirements of (), national schistosomiasis surveillance sites were assigned in all schistosomiasis-endemic counties (cities, districts) and the potential endemic counties (cities, districts) in the Three Gorges Reservoir areas, and snail status was monitored according to different epidemic types. In endemic areas, snail survey was performed by means of systematic sampling and environmental sampling, and the occurrence of frames with snails and the prevalence of infections in snails were calculated, while in potential endemic areas, the risk of imported snails and snails in floating debris were monitored.
snail survey was performed covering an area of 116 834.16 hm in the national schistosomiasis surveillance of China from 2015 to 2019, with 35 007.62 hm snail habitats identified. A total of 6 908 292 frames were surveyed during the 5-year period, and there were 364 555 frames detected with snails, with a 5.28% mean occurrence of frames with snails. Among 997 508 living snails captured, no infections were detected, and loop-mediated isothermal amplification (LAMP) assay detected 18 positive mixed snail samples. During the period from 2015 to 2019, 147.20 hm emerging snail habitats were identified, with an overall tendency towards a rise seen in the proportion of emerging snail habitats in plain regions with waterway networks (0.12% to 92.00%), a tendency towards a rise followed by decline seen in marshland and lake regions (0 to 96.72%), and a large fluctuation in hilly regions (0 to 88.49%). A total of 831.10 hm re-emerging snail habitats were found in the national schistosomiasis surveillance sites of China from 2015 to 2019, with an overall tendency towards a rise seen in the proportion of re-emerging snail habitats in marshland and lake regions (16.05% to 79.66%), an overall tendency towards a decline seen in hilly regions (19.25% to 81.00%), and a minor fluctuation in plain regions with waterway networks (1.10% to 10.14%). During the 5-year period from 2015 to 2019, a total of 48 656 kg floating debris were captured in 4 surveillance sites in the Three Gorges Reservoir areas, and 2 204 snails were found, with no snails identified.
The areas of snail habitats tended to be stable in the national schistosomiasis surveillance sites of China during the period from 2015 to 2019, however, there was a gradual rise in the area of snail habitats year by year, and LAMP assay identified positive snail samples, suggesting snail control is far from optimistic in China.
分析2015 - 2019年中国血吸虫病监测点的钉螺监测数据,了解中国血吸虫病流行区钉螺状况变化,为钉螺控制提供科学依据。
按照《全国血吸虫病监测方案》要求,在所有血吸虫病流行县(市、区)及三峡库区潜在流行县(市、区)设立血吸虫病监测点,根据不同流行类型监测钉螺状况。在流行区,采用系统抽样和环境抽样方法进行钉螺调查,计算有螺框出现率和钉螺感染率;在潜在流行区,监测输入性钉螺和漂浮物中钉螺的风险。
2015 - 2019年全国血吸虫病监测共调查面积116 834.16 hm,查出有螺面积35 007.62 hm。5年共调查6 908 292框,查出有螺框364 555框,有螺框平均出现率为5.28%。捕获活螺997 508只,未检测到感染性钉螺,环介导等温扩增(LAMP)法检测出18份阳性混合钉螺样本。2015 - 2019年期间,新发现有螺面积147.20 hm,平原水网地区新发现有螺面积比例呈总体上升趋势(0.12%~92.00%),湖沼地区呈先上升后下降趋势(0~96.72%),山丘地区波动较大(0~88.49%)。2015 - 2019年全国血吸虫病监测点共发现复现性有螺面积831.10 hm,湖沼地区复现性有螺面积比例呈总体上升趋势(16.05%~79.66%),山丘地区呈总体下降趋势(19.25%~81.00%),平原水网地区波动较小(1.10%~10.14%)。2015 - 2019年5年间,三峡库区4个监测点共捕获漂浮物48 656 kg,发现钉螺2 204只,未发现感染性钉螺。
2015 - 2019年中国血吸虫病监测点钉螺面积总体趋于稳定,但有逐年缓慢上升趋势,且LAMP法检测出阳性钉螺样本,提示中国钉螺控制形势不容乐观。