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Human-altered disturbance regimes: Effects of flood control along the Wisconsin River.

机译:人为改变的干扰机制:威斯康星河沿岸的防洪影响。

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Levees have been ignored by ecologists relative to other flood regime alterations such as dams. I examine several of the generally assumed effects of levees and determine their relevance for setback levees, levees further back in the floodplain. First, a hydraulic model is used to determine whether flood-control levees have altered the pattern and frequency of inundation and flood power. Sampling of floodplain forest in the field is used to relate the simulated flood regime to changes in the floodplain forest composition. Increases in flood stage (height) due to levees were minor, only a few centimeters, primarily due to the position of the levees, set back hundreds of meters into the floodplain in some areas. Increases in overbank flood velocities due to levees were minimal compared to increases caused by channel constriction and by increased flood magnitude. Generally, levees had a greater impact on stage and overbank flood velocities of larger magnitude events.; I also created a spatial model of floodplain inundation to examine the effects of levees and dams on the duration and abundance of floodplain pond habitat. The relative and cumulative impacts of levees and dams on the duration of these habitats are unknown. When the levee was breached, no differences were found between the natural and levee floodplain scenarios. Dams either decreased, increased or had no effect on the area occupied by temporary ponds, depending on flood magnitude. Synergistic interactions between levees and dams were apparent for larger flood events, where the reduction in flood stage due to dams preventing levee breaching. Lastly, building on the flood model, I determine how levees and dams have impacted denitrification (or water purification) services provided by floodplain ponds and wetlands. We compared three scenarios: a natural river-floodplain, a leveed floodplain, and a regulated river-floodplain. Total NO3 processing increased with flood magnitude. The percent processed under the three scenarios was similar, also suggesting that the initial mass of NO3 on the floodplain was critical in controlling the total NO3 processed.
机译:相对于其他洪水制度变更(例如水坝),生态学家已经忽略了堤坝。我研究了堤防的几种通常假定的影响,并确定了它们与倒退堤防的相关性,而这些堤防又回到了洪泛区。首先,使用水力模型来确定防洪堤是否改变了洪水和洪水的形式和频率。野外洪泛区森林采样用于将模拟洪水制度与洪泛区森林组成的变化联系起来。由于堤坝的影响,洪水阶段(高度)的增加很小,主要是由于堤坝的位置,仅几厘米,使某些地区的洪水泛滥成百米。与由于河道狭窄和洪水幅度增加引起的堤岸增加相比,堤坝引起的堤岸洪水速度增加很小。通常,堤防对较大规模事件的阶段性洪水和堤岸洪水速度影响更大。我还创建了漫滩泛滥的空间模型,以检查堤坝和大坝对漫滩池塘生境的持续时间和丰富度的影响。堤坝和水坝对这些生境持续时间的相对和累积影响尚不清楚。当堤防被破坏时,自然和堤防洪泛区方案之间没有发现差异。根据洪水的大小,水坝减少,增加或对临时池塘所占面积没有影响。在较大的洪水事件中,堤坝与大坝之间的协同相互作用是显而易见的,因为大坝阻止了堤坝的破坏,洪水期减少了。最后,在洪灾模型的基础上,我确定了堤坝和大坝如何影响洪泛区池塘和湿地提供的反硝化(或水净化)服务。我们比较了三种情况:天然河漫滩,堤坝泛滥和受管制河漫滩。 NO 3 的总处理量随洪水强度的增加而增加。在这三种情况下处理的百分比是相似的,这也表明洪泛平原上NO 3 的初始质量对于控制处理的总NO 3 至关重要。

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