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Management of invasive aquatic weeds with emphasis on biological control in Senegal

机译:管理侵入性水生杂草,重点是塞内加尔的生物控制

摘要

In 1985 the Diama Dam was built near the mouth of the Senegal River to regulate flows during the rainy season and prevent the intrusion of seawater during the dry season. This created ideal conditions upstream of the dam wall for invasion by two highly invasive aquatic weeds, first by water lettuce Pistia stratiotes Linnaeus (Araceae) in 1993, and then by salvinia Salvinia molesta D.S. Mitchell (Salviniaceae) in 1999. This study was focused on the management of P. stratiotes and S. molesta. Following successes that were achieved elsewhere in the world, biological control programmes involving two weevil species were inaugurated against both weeds and research was focused on several aspects. These included pre-release studies to determine the weevils' host-specificity and impact on the plants in the laboratory, their subsequent mass-rearing and releases at selected sites and post-release evaluations on their impact on the weed populations in the field. Both programmes, which reprepresented the first biocontrol efforts against aquatic weeds in Senegal, proved highly successful with severe damage inflicted on the weed populations and complete control achieved within a relatively short time span. A laboratory exclusion experiment with N. affinis on P. stratiotes showed that in treated tubs, the weevil strongly depressed plant performance as measured by the plant growth parameters: mass, rosette diameter, root length, number of leaves and daughter plants whereas control plants were healthy. Field releases started in September 1994 and water coverage by P. stratiotes at Lake Guiers was reduced by 25% in January 1995 and 50% in April 1995. A general decline of 65% in water coverage by P. stratiotes was observed in June 1995 and by August 1995, eight months after releases P. stratiotes mats were destroyed. Further, although no releases were made there, good results were obtained within 18 months at Djoudj Park water bodies, located 150 km NW from Lake Guiers indicating the potential of the weevil to disperse long distances. In 2005, P. stratiotes reappeared and the weevil N. affinis has located and controlled all of these P. stratiotes recurrences after new releases. In 1999, S. molesta covered an estimated area of 18 000 ha on the Senegal River Left Bank and tributaries (Senegal) and 7 840 ha on the Senegal River Right Bank (Mauritania). Military and Civil Development Committee (CCMAD) and community volunteers made an effort to control S. molesta using physical removal, but this costly and labour-intensive approach was unsustainable. Hence, biological control was adopted by Senegal and Mauritania to manage the weed. Host range tests to assess feeding by C. salviniae on S. molesta and non-target plants and carried out on 13 crop species showed that no feeding damage was observed on the latter and weevils only fed on S. molesta. Field releases of some 48 953 weevils at 270 sites were made from early January 2002 to August 2002. Within one year, weevils were established and were being recovered up to 50 km from the release sites. In a case study conducted at one of the release sites, the S. molesta infestation was reduced from 100% to less than 3% 24 months after release. These results are discussed in the context of the weeds’ negative impact on aquatic systems and riverside communities, and in the involvement of these communities in the programmes.
机译:1985年,在塞内加尔河河口附近修建了Diama大坝,以调节雨季的流量并防止旱季的海水入侵。这为坝壁上游的两个高侵入性水生杂草的入侵创造了理想条件,首先是水生菜Pistia stratiotes Linnaeus(Araceae),然后是Salvinia Salvinia molesta DS Mitchell(Salviniaceae)。1999年。纹状体和mole鼠的管理。在世界其他地方取得成功之后,针对两种杂草的生物防治计划开始了,同时针对杂草进行了研究,并且研究集中在几个方面。其中包括释放前的研究,以确定象鼻虫的宿主特异性及其对实验室植物的影响,随后对它们在选定地点的大量繁殖和释放进行评估,以及释放后评估其对田间杂草种群的影响。这两个方案都代表了塞内加尔对水生杂草的首次生物防治努力,并被证明非常成功,对杂草种群造成了严重破坏,并在较短的时间内实现了全面控制。一项对猪笼草的链霉菌进行的实验室排除实验表明,在处理过的盆中,象鼻虫严重压低了植物的生长性能,这是通过植物生长参数来衡量的:质量,莲座直径,根长,叶片和子代植物的数量,而对照植物是健康。从1994年9月开始释放田野,吉尔斯湖纹状体的水覆盖率在1995年1月减少了25%,在1995年4月降低了50%。1995年6月和2004年观察到纹状体的水覆盖率普遍下降了65%,而到1995年8月,即释放P. stratiotes垫子后八个月。此外,尽管那里没有释放,但在距圭尔湖西北150公里处的Djoudj公园水体中,在18个月内取得了良好的结果,表明象鼻虫有可能散布远距离。在2005年,P。条纹再次出现,象鼻虫N. affinis在新版本发布后找到并控制了所有这些P.条纹复发。 1999年,S。molesta覆盖塞内加尔河左岸和支流(塞内加尔)的估计面积为18 000公顷,塞内加尔河右岸(毛里塔尼亚)的面积为7 840公顷。军事和民用发展委员会(CCMAD)和社区志愿者努力通过物理去除来控制葡萄球菌,但是这种昂贵且劳动密集的方法是不可持续的。因此,塞内加尔和毛里塔尼亚采用了生物防治方法来治理杂草。寄主范围测试评估了沙门氏菌对S. molesta和非目标植物的摄食,并对13种农作物进行了试验,结果表明在后者身上未观察到饲喂损害,而象鼻虫仅对S. molesta摄食。从2002年1月上旬至2002年8月,在270个地点对48 953只象鼻虫进行了现场释放。一年之内,建立了象鼻虫,并在距释放点50 km的地方将其回收。在其中一个释放地点进行的案例研究中,释放后24个月,葡萄球菌的侵扰从100%减少到不足3%。在杂草对水生系统和河沿社区的负面影响以及这些社区参与计划的背景下讨论了这些结果。

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    Diop Ousseynou;

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  • 年度 2007
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