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Fig 1.

Location of the Chequamegon-Nicolet National Forest and the northern Wisconsin stream network.

Streams surveyed during fall for active beaver colonies on the Chequamegon-Nicolet National Forest. Targeted streams are in magenta and non-targeted streams are in green. The grey background for the stream network is the topography of northern Wisconsin as represented by a hillshade model. Weather data were obtained from the indicated National Weather Service Cooperative Observer Program (COOP) weather stations.

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Fig 1 Expand

Table 1.

Effort for aerial surveys of beaver colonies made October–November along four categories of streams in the Chequamegon-Nicolet National Forest, 1987–2013 (Nicolet side) and 1997–2013 (Chequamegon side).

Targeted streams were subject to the beaver control program.

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Table 1 Expand

Table 2.

Variables used to assess the ability of weather to explain minor variations in the beaver density index on non-managed streams or function as drivers of trends on those streams.

Each variable was computed for the current year and the three preceding years. Variables were standardized against their long-term averages (1983–2013).

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Table 2 Expand

Fig 2.

Beaver colony numbers/km by year for (a) trout streams without targeted beaver management and (b) trout streams with targeted beaver management for the Chequamegon-Nicolet National Forest.

In panel (a), open circle = Nicolet trout streams, filled circle = Nicolet non-trout streams, open square = Chequamegon trout streams, filled square = Chequamegon non-trout streams. In panel (b), open circle = Nicolet side, triangle = Chequamegon side. Dotted lines are the predicted trends from generalized additive models (significant trends only).

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Fig 2 Expand

Table 3.

Weather models for beaver colony density on streams where no targeted beaver management occurred on the Chequamegon side of the Chequamegon-Nicolet National Forest, 1997–2013.

Models listed are the minimum AIC model, competitive models (those models within 2 AC units of the 006Dinimum), and the 2007 drought model. The evidence ratio is the ratio of the Akaike weights for the minimum AIC model and an alternate model.

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Table 4.

Time trend and weather models for beaver colony density on streams where no targeted beaver management occurred on the Nicolet side of the Chequamegon-Nicolet National Forest, 1987–2013.

Models listed are the minimum AIC model, competitive models (those models within 2 AC units of the minimum), and the trend model.

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