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Range map. Pink color indicating exotic species.
Habitat and Range
Brown trout occupy a range of aquatic systems and habitats from coldwater mountain streams to larger rivers, ponds and lakes. Within the park, brown trout have successfully colonized the lower gradient reaches of the Rose and Hughes Rivers since initial stockings in the 1960s and more recently have invaded upstream into Brokenback Run from its confluence with the Hughes. There is also a naturalized population of browns within a section of the ConwayRiver that serves as a common boundary between the park and the Rapidan Wildlife Management Area, owned by Virginia. Naturalized brown trout populations historically occurred within the park in the North Fork Moorman’s River and in the North ForkThorntonRiver but have since declined within both and are believed to have been extirpated. The Moorman’s population likely perished starting with the 1995 flood event followed by severely reduced subterranean flows during drought years that persisted through 2002. The magnitude of the population that persisted within the ThorntonRiver from initial stocking in the 1960s is unknown but that population apparently perished by about 1990.
Brown trout are considered native in Iceland, Europe, western Asia and northwestern Africa. These highly adaptable trout have been extensively introduced and now occur on every major continent except Antarctica. Brown trout have been propagated within North America since the late 1800s including the state of Virginia. The most widespread introductions of brown trout into Virginia waters including streams that originate within the park occurred after 1960.
Behavior
Unlike brook trout , brown trout will actively feed during daylight hours so long as they are undisturbed. Only the largest fish typically transition into deeper waters or become more active at night. Brown trout are however more associated with streambed or benthic habitats than are brook or rainbow trout. In heavily fished waters, brown trout become increasingly wary and very selective in which food items they will and will not respond to.
Due to a combination of size and diet, brown trout often displace native brook trout where the two species overlap. They tend to dominate the best available habitat by either forcing brook trout from preferred habitat and, to an extent, by preying directly upon brook trout.
Diet
Brown trout feeding strategies and diet differ with respect to their size. Generally, brown trout less than 12 inches feed primarily on insects drifting freely within stream currents. Above 12 inches generally, brown trout diets shift to larger prey items including crayfish and other fish, including other trout. Other occasional prey items include mollusks, salamanders, frogs and small mammals.
Ecosystem Role
Because brown trout are large, non-native and dominant predatory fish, they are a threat to native fish populations, particularly within the confines of small, mountain stream habitats. In turn, the smaller and intermediated sized brown trout are preyed upon by northern water snakes, mink, kingfishers, herons and the occasional otter within ShenandoahNational Park. As is true for brook trout within park streams, the northern water snake is very likely responsible for a fairly high percentage of brown trout predation within the park. While conducting brown trout removals within RoseRiver in 2006, the fish crew observed a large water snake in the process of engulfing an 8 to 9 inch brown trout that it had recently captured.
Threats
Brown trout are wily, large and highly prized game fish. The presence and proliferation of exotic brown trout has the potential to impact brook trout and other native fish populations within several of the park’s premier large streams. Currently, the brown trout issue is confined to the lower reaches of three park streams. Brown trout have demonstrated the potential to displace brook trout from entire sections of those three streams that currently contain established brown trout populations.
There is growing interest from the Virginia Department of Games and Inland Fisheries in the production and ultimately the stocking of triploid (reproductively sterile) brown trout in selective streams in western Virginia including a number of streams that originate in the park. The appeal of triploid fish from an angler’s point of view is that they experience more rapid growth rates since the energy typically associated with reproductive cycles would instead be available for growth. The principal threats associated with the stocking of triploid brown trout results from their ability to hold over well in a stream following release as they are more difficult to catch. Ultimately, the presence of large brown trout adjacent to populations of wild brook trout may result in encroachment that leads to displacement via domination or predation.
Like brook trout , brown trout are somewhat tolerant of acidified waters. Brown trout are also likewise subjected to sudden and sometimes dramatic changes in population as the result of severe flood and drought events.
References
Atkinson, J.B. 2005. Shenandoah National Park Fisheries Monitoring Program Annual Report for 2004. Division of Natural and Cultural Resources, Luray, Virginia 22835. 46 pp.
Jenkins, R.E., and N.M. Burkhead. 1993. Freshwater fishes of Virginia. American Fisheries Society, Bethesda, Maryland. 1079 pp.
Josephson, Dan. 1982. An Evaluation of Sympatric Populations of Brown and Brook Trout in Four Virginia Streams. Dingell-Johnson Project F-39-p-4. M.S. Thesis Virginia Polytechnic Institute and State University.
Virginia Department of Game and Inland Fish Species Description