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Before-after, control-impact analysis of evidence for the impacts of water level on Walleye, Northern Pike and Yellow Perch in lakes of the Rainy-Namakan complex (MN, USA and ON, CA)

机译:前后,对Rainy-Namakan复杂地区(美国明尼苏达州和美国加利福尼亚州)的水位对角膜白斑,北派克和黄鲈影响的证据进行控制影响分析

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摘要

Water level (WL) fluctuations in lakes influence many aspects of ecosystem processes. Concern about the potential impact of WL fluctuations on fisheries was one of the factors that motivated the decision in 2000 to alter the management of WL in the Rainy-Namakan reservoir complex (on the border between the U.S. state of Minnesota and the Canadian province of Ontario). We used a Before-After, Control-Impact (BACI) framework to identify potential impacts of the change in WL management to Walleye, Northern Pike and Yellow Perch catch per unit effort (CPUE). The CPUE of these species from 1990–1999 and from 2005–2014 were compared in four impact lakes (Lake Kabetogama, Namakan Lake, Rainy Lake and Sand Point Lake) and two control lakes (Lake of the Woods and Lake Vermilion) using a simple Bayesian model. Changes in fish CPUE in the impact lakes were often similar to changes that occurred in at least one control lake. The only change that was not similar to changes in control lakes was an increase of Yellow Perch in Lake Kabetogama. The two control lakes often differed substantially from each other, such that if only one had been available our conclusions about the role of WL management on fisheries would be very different. In general, identifying cause-and-effect relationships in observational field data is very difficult, and the BACI analysis used here does not specify a causative mechanism, so co-occurring environmental and management changes may obscure the effect of WL management.
机译:湖泊中的水位(WL)波动会影响生态系统过程的许多方面。对WL波动对渔业的潜在影响的担忧是促使2000年决定改变Rainy-Namakan水库综合设施(位于美国明尼苏达州和加拿大安大略省之间的边界)的WL管理的因素之一。 )。我们使用了“事前,事后控制”(BACI)框架来确定WL管理更改对每单位工作量(CPUE)的Walleye,Northern Pike和Yellow Perch渔获量的潜在影响。使用简单的方法,在四个影响湖(Kabetogama湖,Namakan湖,Rainy湖和Sand Point湖)和两个控制湖(伍兹湖和朱红色湖)中比较了1990-1999年和2005-2014年这些物种的CPUE。贝叶斯模型。冲击湖中鱼类CPUE的变化通常与至少一个对照湖中发生的变化相似。与控制湖变化不同的唯一变化是Kabetogama湖中的黄鲈的增加。这两个控制湖常常彼此之间有很大的不同,因此,如果只有一个控制湖,那么我们关于野生动植物管理在渔业中的作用的结论将大不相同。通常,在观测现场数据中确定因果关系非常困难,并且此处使用的BACI分析未指定原因机制,因此,同时发生的环境和管理变更可能会掩盖WL管理的效果。

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