These data depict the locations (only) of all Brook Trout Genetics study sites in the park. Great Smoky Mountains National Park (GRSM) is committed to monitoring ecological and evolutionary functions and processes of park ecosystems. Brook trout (Salvelinus fontinalis) is the only salmonid native to the Southern Appalachians and functions as a keystone species in some headwater streams. The historic use of hatchery-reared brook trout for supplemental and restorative stocking in GRSM underscores the need to recognize the evolutionary relationship among stream populations. A recent survey of microsatellite DNA variation in GRSM brook trout indicated the presence of highly significant differentiation at all hieratical levels which suggests that the individual stream should be considered the unit of management. Given that management resources are limited and that stream-specific management is often not practical, fisheries managers need to know whether the genetic divergence observed among GRSM brook trout reflect adaptive differences or is the variation due to stochastic processes like random genetic drift. DNA microarrays are a powerful method for the global analysis of steady-state intracellular mRNA levels, and thus identifying genes that are transcriptionally modulated as a consequence of metabolic or bioenergetic demands. The information gathered from these arrays of gene sequences can be used to characterize complex biological processes and interactions providing insight into the adaptive significance of observed genetic differentiation. This research objective, if funded, would represent the first attempt at determining whether GRSM fisheries managers should focus their resources on genetic relatedness or demographics.

The brook trout (Salvelinus fontinalis) is the only trout native to the southern Appalachian Mountains. It was once widespread in Great Smoky Mountains National Park (GRSM), occupying small, swift, high elevation mountain streams as well as larger rivers down to elevations of 1,600 feet. Since 1900, the brook trout has vanished from about 75% of its historical range in GRSM. The initial loss was due to large-scale mechanized logging operations early in the 20th century. Clear cuts and subsequent fires on steep mountainsides led to soil run-off and stream siltation. In addition, trees were cut from stream banks, allowing more sunlight to reach the waterways and raising water temperatures. The brook trout is even less tolerant of warm water than other trout species- it can not survive temperatures above 68˚F. (20˚C). As a result of these environmental changes, the brook trout disappeared from all streams in the Smokies below elevations of 3,000 feet. The decline of the brook trout caused displeasure among anglers who longed to trout fish in the mountains. In response, around 1910, logging companies and other entities began stocking streams with non-native rainbow trout from the western United States, brown trout from Europe, and brook trout from the northern United States. Stocking of northern brook trout continued into the 1950s; rainbow trout stocking did not cease until 1975. Competition from the non-native trout, especially rainbows, lead to further declines in the brook trout population. Rainbow trout are larger, more aggressive fish which dominate the prime habitats in streams and eat small brook trout. Biologists believe brook trout range in the Smokies has declined dramatically due to rainbow competition. Most surviving brook trout have become confined to marginal streams above 3,500 feet in elevation. Stream acidification is an increasingly serious threat to the survival of brook trout. Streams in GRSM naturally become more acidic at higher elevations. However, research shows that areas in the park above 4,800 feet in elevation are receiving some of the highest amounts of acid rain, acid fog, and dry deposition of any monitored site in North America. Consequently, many high elevation streams are becoming increasingly acidic, some to the point that they can no longer support brook trout. In 1996, genetic research conducted by the University of Tennessee confirmed long-held beliefs that the southern Appalachian brook trout is a distinct subspecies, differing in several ways from the stocked fish native to the northeastern United States and Canada. Only about 15% of park streams are believed to harbor pure strains of truly native fish, undiluted by hybridization with northern brook trout. Since the southern subspecies has such a limited range, and because that range has been diminished drastically in the last 100 years, the southern brook trout is considered a species of special concern. The Park Service is especially watchful of acidification and competition from rainbow trout in streams where the subspecies currently survives. Why Monitor Distribution? It has been determined that native brook trout have lost approximately 75% of their range and that 30 species of non-game fish are missing from the Park as a result of man-induced changes in the landscape. Unfortunately, annual monitoring to assess changes in aquatic communities were not implemented until the mid-1980’s. The efforts resulted in the development of standardized sampling protocols for streams in GRSM. The value of these protocols was quickly recognized by state and federal agencies working with trout resources elsewhere in the southeast. The protocols formed the basis of the “Standardized Sampling Guidelines for Wadeable Trout Streams” (Appendix B) which were adopted by the Trout Committee of the Southern Division of the American Fisheries Society. These protocols have been well tested and provide a method that adequately evaluates annual variation in fish

For depicting the extent of fish distribution 2015 (Brook, Brown, and Rainbow) in the Great Smoky Mountains National Park. Using the USGS HEM Event Management tool, the start and end point of fish species are identified on named and un-named rivers and streams in the park. The HEM tool uses linear referencing to create linear feature class data which depicts the extent of fish distribution within the stream network. The EVENTTYPE attributes lists the fish species and can be used in combination with attribute queries to create one or many species distribution maps. These data support an on-going project and are published online to support project operational needs. As such, these data are not considered valid or final and may contain omissions or errors. Background and HistoryThe brook trout (Salvelinus fontinalis) is the only trout native to the southern Appalachian Mountains. It was once widespread in Great Smoky Mountains National Park (GRSM), occupying small, swift, high elevation mountain streams as well as larger rivers down to elevations of 1,600 feet. Since 1900, the brook trout has vanished from about 75% of its historical range in GRSM. The initial loss was due to large-scale mechanized logging operations early in the 20th century. Clear cuts and subsequent fires on steep mountainsides led to soil run-off and stream siltation. In addition, trees were cut from stream banks, allowing more sunlight to reach the waterways and raising water temperatures. The brook trout is even less tolerant of warm water than other trout species- it can not survive temperatures above 68˚F. (20˚C).As a result of these environmental changes, the brook trout disappeared from all streams in the Smokies below elevations of 3,000 feet. The decline of the brook trout caused displeasure among anglers who longed to trout fish in the mountains. In response, around 1910, logging companies and other entities began stocking streams with non-native rainbow trout from the western United States, brown trout from Europe, and brook trout from the northern United States. Stocking of northern brook trout continued into the 1950s; rainbow trout stocking did not cease until 1975. Competition from the non-native trout, especially rainbows, lead to further declines in the brook trout population. Rainbow trout are larger, more aggressive fish which dominate the prime habitats in streams and eat small brook trout. Biologists believe brook trout range in the Smokies has declined dramatically due to rainbow competition. Most surviving brook trout have become confined to marginal streams above 3,500 feet in elevation.Stream acidification is an increasingly serious threat to the survival of brook trout. Streams in GRSM naturally become more acidic at higher elevations. However, research shows that areas in the park above 4,800 feet in elevation are receiving some of the highest amounts of acid rain, acid fog, and dry deposition of any monitored site in North America. Consequently, many high elevation streams are becoming increasingly acidic, some to the point that they can no longer support brook trout.In 1996, genetic research conducted by the University of Tennessee confirmed long-held beliefs that the southern Appalachian brook trout is a distinct subspecies, differing in several ways from the stocked fish native to the northeastern United States and Canada. Only about 15% of park streams are believed to harbor pure strains of truly native fish, undiluted by hybridization with northern brook trout. Since the southern subspecies has such a limited range, and because that range has been diminished drastically in the last 100 years, the southern brook trout is considered a species of special concern. The Park Service is especially watchful of acidification and competition from rainbow trout in streams where the subspecies currently survives. Why Monitor Distribution?It has been determined that native brook trout have lost approximately 75% of their range and that 30 s

A feature class depicting geographic locations where permanent water quality monitoring locations have been established in Great Smoky Mountains National Park. This includes monitoring location sites established by the National Park Service and other state and federal agencies responsible for water quality monitoring and reporting. Agencies responsible for a monitoring location are listed in the attributes ORGANIZATIONIDENTIFIER and ORGANIZATIONFORMALNAME. For the display, query, and analysis of legacy and current hydrology spatial and tabular data; Consolidate and centralize a very diverse range and quantity of monitoring location site data from numerous programs and protocols; Mitigate the duplication of monitoring location data across shared systems; Allow for single-source identification and management of monitoring location sites that are "co-located"; Provide a single point of data entry, management, query, analysis, and display of water quality data from numerous sources, including STORET which are sourced from an accurate monitoring location database; Enable spatial relationship of water quality monitoring data to High-Resolution USGS NHD Reaches through the use of modern GIS, database, and statistics software; Support USGS and EPA standards for spatial and non-spatial hydrology and water quality data exchange and sharing. Very important details are included in the attached metadata document and should be read thoroughly before these data are used.

Endpoint distribution of Brook and Rainbow Trout in GRSM, 2015.

Nighttime roadside spotlight counts of white-tailed deer in Cades Cove, Great Smoky Mountains National Park

Nighttime roadside spotlight counts of white-tailed deer in Cades Cove, Great Smoky Mountains National Park