1988
DOI: 10.5962/bhl.title.99554
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Recent historical and projected regional trends of trout in the southeastern United States /

Abstract: Forest and Range Experiment Station. 19 p. The recent history of trout in the Southeastern United States is described. A statistical relationship established between current trout density and land use and forest cover in watersheds is the core of a projection tool that evaluates impacts of expected future and alternative timber management on trout for regional and national assessments.

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Cited by 4 publications
(9 citation statements)
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“…However, spatial patterns of habitat loss predicted by our reach models suggest that a warming climate will increase stream network fragmentation and isolation of brook trout populations. At the watershed scale, brook trout habitat is already highly fragmented throughout much of the historical range due to deforestation, water pollution, and the paucity of connected cold‐water mainstems (Flebbe et al 1988, , Stranko et al 2008). Our results suggest that additional fragmentation within headwater streams may become increasingly important over time.…”
Section: Discussionmentioning
confidence: 99%
“…However, spatial patterns of habitat loss predicted by our reach models suggest that a warming climate will increase stream network fragmentation and isolation of brook trout populations. At the watershed scale, brook trout habitat is already highly fragmented throughout much of the historical range due to deforestation, water pollution, and the paucity of connected cold‐water mainstems (Flebbe et al 1988, , Stranko et al 2008). Our results suggest that additional fragmentation within headwater streams may become increasingly important over time.…”
Section: Discussionmentioning
confidence: 99%
“…This wild trout range was known to include many streams that do not actually have trout. Wild trout predominantly occur in southern Appalachian streams within forested watersheds rather than in streams associated with agricultural and developed human land uses (Flebbe et al 1988;Harding et al 1998). We used the 1992 National Land Cover Data Set of USGS and EPA (MLCD Consortium 2001) to identify the following areas within the wild trout boundary map that were considered to be unsuitable for trout because surrounding land cover was not forested: developed (classes 21-23); barren (31-33); orchards, vineyards, etc.…”
Section: Methodsmentioning
confidence: 99%
“…Most models of trout distribution in a warmer climate are based on the analysis of trout range in an area (Meisner 1990;Keleher and Rahel 1996;Clark et al 2001), assuming that this range is homogeneously suitable trout habitat. However, trout habitat is associated with mature forest and not with human-dominated land cover (Flebbe et al 1988), and fragmentation of suitable land cover on the landscape will probably exacerbate effects of climate change (Opdam and Wascher 2004). Land cover (herein, we use ''land cover'' in place of ''land cover and land use'') information can be combined with trout distribution range information to map trout habitat in the region to more accurately assess how trout habitat would shrink in a warmer climate.…”
mentioning
confidence: 96%
“…However, studies have been conducted on a limited geographic area in and near the Great Smoky Mountains National Park of North Carolina and Tennessee (e.g., Moore et al 1983Moore et al , 1986Bivens et al 1985;Larson and Moore 1985) and were not designed to consider patterns over the full range of latitudinal and elevational gradients in the region. Yet, the southern Appalachian region, from northern Virginia to northern Georgia, extends 700 km over 5° of latitude and includes thousands of kilometers of trout stream (Flebbe et al 1988). Other studies have shown brook trout to be widely distributed and abundant in the Shenandoah National Park of Virginia (500 km north of Great Smoky Mountains National Park), where rainbow trout are rare and of limited distribution (Lennon 1961).…”
mentioning
confidence: 99%