首页> 外文期刊>Journal of Aquatic Plant Management >Overwinter habitat and the relationship of overwinter to in-lake densities of the milfoil weevil, Euhrychiopsis lecontei, a Eurasian watermilfoil biological control agent
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Overwinter habitat and the relationship of overwinter to in-lake densities of the milfoil weevil, Euhrychiopsis lecontei, a Eurasian watermilfoil biological control agent

机译:过冬栖息地与冬季冬季密度的关系,欧洲摩尔菲利药物的母乳喂养莱氏虫湖湖密度

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The native weevil Euhrychiopsis lecontei has been associated with declines of Eurasian watermilfoil (Myriophyllum spicatum). The weevil spends all summer on submersed plants, producing 3 to 6 generations. In September to November adult weevils moveto shore where they overwinter in leaf litter at drier sites near the shoreline. Mean November shoreline densities from 1992-1998 at Lake Auburn (mean = 43 N/m~2) and Smith's Bay of Lake Minnetonka, (mean = 125 N/m~2) have ranged from zero to over 200 N/m~2. Overwinter mortality is not severe (survival was typically >60 percent). Adults collected from terrestrial habitat have developed flight muscles and limited flight has been observed in the spring but submersed adults in summer do not have developedflight muscles. Adults return to the water in spring and females begin to develop and lay eggs after the water temperature reaches 10-15C. Spring (May-June) and Fall (September) inlake densities in these two lakes have ranged from zero to 40 N/m~2 and Lake Auburn typically had higher in-lake weevil densities (mean of 15 N/m~2 compared to 4 N/m~2 at Smith's Bay). There was no relationship between in-lake and shoreline densities at Lake Auburn, but Smith's Bay spring in-lake densities were correlated withspring shoreline densities. Inlake densities were not correlated between the two lakes but shoreline densities were correlated over time, suggesting that regional climatic factors may influence shoreline densities. Weevils disappeared from Lake Auburn in-lake samples in July 1998; no weevils were found there in shoreline or in-lake samples in 1999. In-lake factors such as fish predation may be more limiting than overwinter conditions.
机译:本土象鼻虫Euhrychiopsis Lecontei与欧亚西海尿素(Myriophyllum Spicatum)的下降有关。象鼻虫在潜水厂夏季,生产3至6代。 9月至11月至11月成人的象鼻虫Moveto岸边,在海岸线附近的干燥场地,他们在叶子垃圾中冬季冬天。意思是11月1992-1998的海岸线密度在Auburn湖(平均= 43 N / M〜2)和史密斯的Minnetonka湖(平均= 125 n / m〜2),从零到200k / m〜2 。过冬死亡率不严重(存活通常> 60%)。从陆地栖息地收集的成年人已经开发了飞行肌肉,在春季观察到有限的航班,但夏天的潜水成年人没有发达的肌肉。成年人在水温达到10-15℃后,春天和女性返回水,雌性开始开发和产卵。春天(五月六月)和秋季(9月)这两个湖泊中的印的印度浓度从零到40 n / m〜2,奥本湖通常具有较高的湖泊象鼻虫密度(与...相比,平均15 n / m〜2)史密斯湾的4个/ m〜2)。在奥本湖湖和海岸线密度之间没有任何关系,但史密斯的海湾春天的湖泊密度与他们的海岸线密度相关。在两个湖泊之间不相关,而且随着时间的推移,海岸线密度无关,这表明区域气候因素可能会影响海岸线密度。 1998年7月,象鼻虫从湖奥本样品湖中消失了; 1999年海岸线或湖中样品中没有发现象鼻虫。如湖泊因素,如鱼类捕食可能比过冬条件更加限制。

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