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Initial Impact of the Gabíkovo Hydroelectric Scheme on the Species Richness and Composition of 0+ Fish Assemblages in the Slovak Flood Plain, River Danube

机译:加比科沃水电计划对多瑙河斯洛伐克洪水平原的物种丰富度和0+鱼类组成的初步影响

摘要

Relatively little information exists on the effects of hydroelectric schemes on 0+ fish composition in large European rivers because few or no pre-impact data exist. We compared 0+ fish species richness and composition, relative density, fish size as well as available and used habitat using data from 12 floodplain sites sampled just prior to (1992) and four years after (1996) the start of operations of the Gabíkovo hydropower station on the River Danube (Slovakia). We also used modelling techniques to assess the change in species richness and habitat use and to predict 1996 occurrences from the 1992 data set. The floodplain was greatly modified by the hydroscheme. Only 12 of 27 sites sampled in August 1992 were extant in August 1996. Therefore, all four channel types identified (flowing, abandoned, weir, wing-dam) were more lentic in 1996 than in 1992, with increased width, smaller-sized sediment (silt, clay) and greater amounts of macrophytes. After the operations of the hydroscheme, the overall relative density of fishes (individuals per surface area) of all ages decreased, with the exception of 0+ fishes, despite a slight reduction in 0+ fish density in all channel types except weirs. Species number increased from 25 to 28, although in all channel types there was a change in the composition of the 0+ fish assemblages, with rheophiles generally replaced by limnophiles and migrants from the lower Danube. The two most important microhabitat variables were the proportion of macrophytes and gravel, the latter being the factor distinguishing 0+ fish microhabitat use in 1992 (preferences) and 1996 (indifference or avoidance). Species richness and 0+ fish density in 1996 could be predicted from the 1992 data using simple log-linear models (density, richness, sample number). Species-specific occurrence in 1996 could not be predicted using environmental/fish data from 1992 with multiple regression or generalized additive models (GAM). However, the overall GAM from 1992 could predict overall fish occurrence in 1996.
机译:在欧洲大型河流中,关于水力发电计划对0+鱼组成的影响的信息相对较少,这是因为几乎没有或没有影响前数据。我们使用Gabíkovo水电站开始运行之前(1992年)和四年后(1996年)采样的12个洪泛区地点的数据,比较了0+种鱼类的丰富度和组成,相对密度,鱼的大小以及可用和使用的栖息地。多瑙河(斯洛伐克)上的火车站。我们还使用建模技术来评估物种丰富度和栖息地使用的变化,并根据1992年的数据集预测1996年的事件。洪泛区被水化学法极大地改变了。在1992年8月采样的27个站点中,只有12个站点在1996年8月存在。因此,与1992年相比,1996年确定的所有四个流道类型(流动,废弃,堰,翼坝)的透镜体都更大,宽度增加,沉积物尺寸更小(淤泥,粘土)和大量的大型植物。进行水化法操作后,所有年龄段的鱼类的总体相对密度(每个表面积的个体)均下降,除了0+条鱼类外,尽管除堰外所有渠道类型的0+鱼类密度均略有降低。物种数量从25种增加到28种,尽管在所有渠道类型中,0 +鱼群的组成都有变化,嗜盐菌通常被嗜盐菌和来自多瑙河下游的移民所取代。两个最重要的微生境变量是大型植物和砾石的比例,后者是区分0+鱼微生境使用的因素(1992年(首选)和1996年(疏忽或避免))。可以使用简单的对数线性模型(密度,丰富度,样本数量)从1992年的数据预测1996年的物种丰富度和0+鱼类密度。使用1992年的环境/鱼类数据,多重回归或广义加性模型(GAM)无法预测1996年特定物种的发生。但是,1992年的总体GAM可以预测1996年鱼类的总体发生。

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