国际流行病学传染病学杂志
國際流行病學傳染病學雜誌
국제류행병학전염병학잡지
INTERNATIONAL JOURNAL OF EPIDEMIOLOGY AND INFECTIOUS DISEASE
2015年
2期
95-98
,共4页
许凤鸣%章柳红%秦家胜%陆红妹%曹为民%陆勤南%蒋亚娟%谢广平
許鳳鳴%章柳紅%秦傢勝%陸紅妹%曹為民%陸勤南%蔣亞娟%謝廣平
허봉명%장류홍%진가성%륙홍매%조위민%륙근남%장아연%사엄평
血吸虫病%水库工程%钉螺%监测
血吸蟲病%水庫工程%釘螺%鑑測
혈흡충병%수고공정%정라%감측
Schistosomiasis%Reservoir project%Oncomelania%Monitoring
目的 掌握合溪水库区域螺情和病情现状,为调整血吸虫病监测方案,建立预警机制提供依据.方法 2009-2014年,选择合溪水库库区、上游集雨区及下游影响区为监测范围,采用常规法进行钉螺监测和人畜病情监测;2014年5-7月和9月,选择合溪水库主要水系南溪和北溪的源头、中段、入库前1 km、入库口、库岸以及出库河道等6段设15个监测点,采用稻草帘进行水体钉螺监测,同时打捞南、北溪入库口和库区漂浮物进行水体钉螺监测.结果 水库建设前(2009年),在水库上游集雨区、库区及下游均查到钉螺,有螺面积分别占81.62%、15.28%、3.10%.水库运行期(2011-2014年),在水库库区及水库下游开展螺情监测,结果均未查到钉螺,有螺面积全部分布在上游集雨区域,2014年钉螺面积7.69 hm2,较2009年(10.34 hm2)下降了25.63%;上游活螺密度2014年为0.08只/0.1m2,较2009下降了87.10%.病情监测结果未发现血吸虫病和病畜.15个监测点均未发现钉螺.结论 合溪水库运行后,库尾、消落带及水库下游钉螺已得到有效控制,水库上游集雨区尚有较大面积钉螺,需建立新的螺情监测、控制和预警机制.
目的 掌握閤溪水庫區域螺情和病情現狀,為調整血吸蟲病鑑測方案,建立預警機製提供依據.方法 2009-2014年,選擇閤溪水庫庫區、上遊集雨區及下遊影響區為鑑測範圍,採用常規法進行釘螺鑑測和人畜病情鑑測;2014年5-7月和9月,選擇閤溪水庫主要水繫南溪和北溪的源頭、中段、入庫前1 km、入庫口、庫岸以及齣庫河道等6段設15箇鑑測點,採用稻草簾進行水體釘螺鑑測,同時打撈南、北溪入庫口和庫區漂浮物進行水體釘螺鑑測.結果 水庫建設前(2009年),在水庫上遊集雨區、庫區及下遊均查到釘螺,有螺麵積分彆佔81.62%、15.28%、3.10%.水庫運行期(2011-2014年),在水庫庫區及水庫下遊開展螺情鑑測,結果均未查到釘螺,有螺麵積全部分佈在上遊集雨區域,2014年釘螺麵積7.69 hm2,較2009年(10.34 hm2)下降瞭25.63%;上遊活螺密度2014年為0.08隻/0.1m2,較2009下降瞭87.10%.病情鑑測結果未髮現血吸蟲病和病畜.15箇鑑測點均未髮現釘螺.結論 閤溪水庫運行後,庫尾、消落帶及水庫下遊釘螺已得到有效控製,水庫上遊集雨區尚有較大麵積釘螺,需建立新的螺情鑑測、控製和預警機製.
목적 장악합계수고구역라정화병정현상,위조정혈흡충병감측방안,건립예경궤제제공의거.방법 2009-2014년,선택합계수고고구、상유집우구급하유영향구위감측범위,채용상규법진행정라감측화인축병정감측;2014년5-7월화9월,선택합계수고주요수계남계화북계적원두、중단、입고전1 km、입고구、고안이급출고하도등6단설15개감측점,채용도초렴진행수체정라감측,동시타로남、북계입고구화고구표부물진행수체정라감측.결과 수고건설전(2009년),재수고상유집우구、고구급하유균사도정라,유라면적분별점81.62%、15.28%、3.10%.수고운행기(2011-2014년),재수고고구급수고하유개전라정감측,결과균미사도정라,유라면적전부분포재상유집우구역,2014년정라면적7.69 hm2,교2009년(10.34 hm2)하강료25.63%;상유활라밀도2014년위0.08지/0.1m2,교2009하강료87.10%.병정감측결과미발현혈흡충병화병축.15개감측점균미발현정라.결론 합계수고운행후,고미、소락대급수고하유정라이득도유효공제,수고상유집우구상유교대면적정라,수건립신적라정감측、공제화예경궤제.
Objective To understand the distribution of oncomelania and the current situation of schistosomiasis of Hexi reservoir,in order to adjust schistosomiasis monitoring programs in this region timely,and provide the basis for establishment of early warning system.Methods The conventional methods were used to monitor human and animal schistosomiasis disease in the upstream area,the reservoirs and the downstream area from 2009 to 2014.Fifteen sites from 6 areas such as the source,the middle,1 km from the storage port,storage port of the south stream and the north stream and so on were selected to monitor the number of oncomelania.The floating debris was fished from the storage port of the south stream and the north stream as well as the reservoir area from May to July,and September 2014.Results The areas with snails accounted respectively for 81.62%,15.28%,and 3.10% in the upstream area,the project area (the bottom,the tail,the fluctuating zone and the dam area) and the downstream area before the Hexi reservoir was built (2009).There was no oncomelania found in the reservoir area (the tail,the fluctuating zone and the dam area) and the downstream area in the reservoir operation period during 2011-2014.The areas of snail were all distributed in the upstream catchment area.The area of oncomelania was 7.69 hm2 in 2014 which decreased 25.63%,compared with 10.34 hm2 in 2009.The density of living snails de creased 87.10% in the upstream area from 2009 to 0.8/0.1 m2 in 2014.There were no patient suffered from schistosomiasis and sick animal found in this monitor.There were no infected oncomelanias found in 15 monitoring sites.Conclusions The effect of schistosomiasis control projects in Hexi reservoir was remarkable for prevention of oncomelania in the tail and the downstream of the reservoir.The establishment of a new snail monitor,control and early warning mechanisms is very urgent because of the large area of oncomelania in the upstream catchment area.