首页> 外文会议>Conference on Fish Telemetry >Effect of hydropeaking on migrations and home range of adult Barbel (Barbus barbus} in the river Meuse
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Effect of hydropeaking on migrations and home range of adult Barbel (Barbus barbus} in the river Meuse

机译:水质烧制对河流河流迁徙和家庭范围的影响

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The non-navigable part of the River Meuse, forming the border between Belgium and the Netherlands, is 60 to 100 metres wide and has an average slope of 0.45 mkirr~(-1). The river has been modified by gravel extraction, bank stabilization, summer dykesand flow modifications. To document fish use of this system, fourteen adult and female (Fork Length: 47.5-57 cm) barbel (Barbus barbus) were radio tagged (40 MHz): 5 in May 2001, 3 in October 2001 and 6 in April 2002. From May 2001 till September 2002 fishes were localized weekly throughout the year and daily in April and May to identify spawning grounds and investigate seasonal migrations and home range. In winter, when flows ranged from 250 to 2 800 m~2s~(-1), barbel were found in the main river bedat all times. No downstream migrations to sheltered parts of the river were observed. In spring, both upstream (0.2 km) and downstream (up to 2.6 km) migrations to spawning grounds were observed. Individual barbel, in the mouth of a tributary, showed different migrations towards spawning areas and holding locations under low flow conditions. Migrations in summer and autumn were directed by changes in flow and habitat suitability. The home ranges of the barbel ranged from 1.05 to 27.3 km and differed significantly in size for different parts of the river. Resident habitat suitability is determined by discharge, water depth, water current and bottom structure. Total home ranges of barbel, occupying a highly structured part in the river with continuous availability of suitable habitat for spawning, resting and foraging were significantly smaller (1490 m) than those for barbel initially caught in areas with less habitat diversity (12.5 km).
机译:河流的不通航部分,形成比利时和荷兰之间的边界,宽度为60至100米,平均斜率为0.45 mkIrr〜(-1)。河流已被砾石提取,银行稳定,夏季堤和流程修改改装。要记录该系统的鱼类使用,14名成人和女性(叉子长度:47.5-57厘米)杠铃(芭巴顶助地)是收音机(40 MHz):5月3日,2001年10月3日,2002年4月3日。来自2001年5月至2002年9月,鱼类每周都在全年本地,每天4月,并可识别产卵场,调查季节迁徙和家庭范围。在冬天,当流量从250到2 800 m〜2s〜(-1)时,杠铃都在主要的河床床上繁忙。没有观察到河流庇护的下游迁移。在春天,观察到上游(0.2公里)和下游(高达2.6公里)迁移到产卵场。在支流口中的单个杠铃显示出不同迁移到产卵区域和在低流量条件下保持位置。夏季和秋季的迁移是通过流动和栖息地适用性的变化。杠铃的家庭范围从1.05到27.3公里范围从1.05到27.3公里,不同的河流不同地区的大小差异。居民栖息地适用性由排放,水深,水流和底部结构决定。杠杆的总套房范围,占据了河流的高度结构化部位,持续适当的栖息地用于产卵,休息和觅食的栖息地显着较小(1490米),而不是杠杆队的栖息地捕获(12.5公里)。

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