中国血吸虫病防治杂志
中國血吸蟲病防治雜誌
중국혈흡충병방치잡지
CHINESE JOURNAL OF SCHISTOSOMIASIS CONTROL
2014年
2期
132-136
,共5页
夏爱%黄轶昕%蒋军%赵亚民%杭德荣%陶恒业%张联恒
夏愛%黃軼昕%蔣軍%趙亞民%杭德榮%陶恆業%張聯恆
하애%황질흔%장군%조아민%항덕영%도항업%장련항
钉螺%长江下游%湿地%生态保护
釘螺%長江下遊%濕地%生態保護
정라%장강하유%습지%생태보호
Oncomelania snail%Lower reaches of the Yangtze River%Wetland%Ecological protection
目的:了解长江下游洲滩湿地和钉螺分布情况,探讨洲滩湿地钉螺控制对策。方法现场调查长江润洲段主江堤外洲滩湿地分布,并按照我国湿地分级式分类系统进行湿地分类;调查2004-2013年润洲段沿江洲滩湿地钉螺面积、钉螺密度及灭螺资料,分析沿江洲滩湿地钉螺消长趋势。结果长江下游润洲段洲滩属河流湿地,除永久性水域外,历史上均有钉螺孳生。现有自然湿地1303.0 hm2,人工湿地1479.0 hm2,功能改变为非湿地1059.0 hm2;2013年查出钉螺面积181.40 hm2,均分布于自然湿地。2004-2013年共计开展药物灭螺和环境改造4624.55 hm2,钉螺面积和钉螺密度下降率分别为66.53%和77.66%。现有钉螺均分布于自然湿地。结论人工湿地有助于钉螺控制,沿江洲滩湿地钉螺控制必须重视湿地生态保护。
目的:瞭解長江下遊洲灘濕地和釘螺分佈情況,探討洲灘濕地釘螺控製對策。方法現場調查長江潤洲段主江隄外洲灘濕地分佈,併按照我國濕地分級式分類繫統進行濕地分類;調查2004-2013年潤洲段沿江洲灘濕地釘螺麵積、釘螺密度及滅螺資料,分析沿江洲灘濕地釘螺消長趨勢。結果長江下遊潤洲段洲灘屬河流濕地,除永久性水域外,歷史上均有釘螺孳生。現有自然濕地1303.0 hm2,人工濕地1479.0 hm2,功能改變為非濕地1059.0 hm2;2013年查齣釘螺麵積181.40 hm2,均分佈于自然濕地。2004-2013年共計開展藥物滅螺和環境改造4624.55 hm2,釘螺麵積和釘螺密度下降率分彆為66.53%和77.66%。現有釘螺均分佈于自然濕地。結論人工濕地有助于釘螺控製,沿江洲灘濕地釘螺控製必鬚重視濕地生態保護。
목적:료해장강하유주탄습지화정라분포정황,탐토주탄습지정라공제대책。방법현장조사장강윤주단주강제외주탄습지분포,병안조아국습지분급식분류계통진행습지분류;조사2004-2013년윤주단연강주탄습지정라면적、정라밀도급멸라자료,분석연강주탄습지정라소장추세。결과장강하유윤주단주탄속하류습지,제영구성수역외,역사상균유정라자생。현유자연습지1303.0 hm2,인공습지1479.0 hm2,공능개변위비습지1059.0 hm2;2013년사출정라면적181.40 hm2,균분포우자연습지。2004-2013년공계개전약물멸라화배경개조4624.55 hm2,정라면적화정라밀도하강솔분별위66.53%화77.66%。현유정라균분포우자연습지。결론인공습지유조우정라공제,연강주탄습지정라공제필수중시습지생태보호。
Objective To understand the distribution of the river beach wetlands and Oncomelania snails in the lower reach-es of the Yangtze River,and explore the countermeasures of snail control. Methods The river beach wetlands outside the Yang-tze River levee were investigated and classified according to the hierarchical and classification system of wetlands of China. The snail survey was carried out in the beach wetlands of Runzhou section of lower reaches of the Yangtze River from 2004 to 2013. The change trend of snail areas and the densities was analyzed in the wetlands. Results The river beach of Runzhou section of lower reaches of the Yangtze River belongs to the riverine wetland. There was Oncomelania snail breeding except the permanent wa-ter area. At present,there were natural wetlands of 1 303.0 hm2,human-made wetlands of 1 479.0 hm2 and wetland function chang-es of 1 059.0 hm2 in the river beach of Runzhou section. There was the snail area of 181.4 hm2 in the natural wetland in 2013. The area of snail control by the molluscicide and environmental modification was 4 624.55 hm2 from 2004 to 2013. The decline rates of snail areas and densities were 66.53%and 77.66%respectively. The existing Oncomelania snails were distributed in the natural wetlands. Conclusion The human-made wetland is helpful to snail control. The snail control in the river beach wetlands should attach a great importance to the protection of wetland ecology.