The snail darter (Percina tanasi) is a species of fish that is found in East Tennessee freshwater in the United States. It is in the perch family (family Percidae) of the order Perciformes. Discovered in 1973, the snail darter was listed as endangered under the U.S. Endangered Species Act of 1973 by 1975 and was involved in a legal controversy leading to a Supreme Court ruling to approve the completion of Tellico Dam, which posed a risk of extinction for the snail darter by blocking its migratory route — see Tennessee Valley Authority v. Hill, snail darter controversy.
In 1978, the U.S. Fish and Wildlife Service, Tennessee Valley Authority (TVA), and Tennessee Wildlife Resource Agency launched a recovery plan to preserve the snail darter by transferring the species to other river systems. Its native range was originally in the lower parts of the Little Tennessee River, the Sequatchie River, and in Chickamauga Creek, but was later eliminated from the Little Tennessee River by the completion of Tellico Dam. The species was then transplanted into the Hiwassee River in southeastern Tennessee. The species inhabits large creeks or deeper portions of rivers and reservoirs with gravel and sand shoals substrate. The snail darter spawns between February to mid-April with the female producing 600 eggs which drift downstream. Juveniles occupy slack water habitats and migrate upstream to the breeding ground. The lifespan of the snail darter ranges between 2 to 4 years. The snail darter adult length ranges between 55 to 90 mm (2.2 to 3.1 inches). The species’ diet consists mostly of snails and insects (caddisflies, midges, and blackflies). Snail darters have camouflage dorsal patterns and burrow in the substrate to conserve energy and hide from predators. They are largely preyed upon by banded sculpin (Cottuss carolinae). The word Tanasi derives from capital of the Cherokee Nation located on the Little Tennessee River where the species was discovered. The species was relisted as threatened in 1984 after being successfully transplanted into other river systems.
The original range of the snail darter was thought to be strictly in the lower portion of the Little Tennessee River with a few individuals dispersing into the headwaters of the Watts Bar Reservoir below Fort Loudon Dam. Prior to the completion of the Tellico dam in 1979, TVA biologists made several efforts to relocate the remaining individuals of the species into other river systems. In 1975 the species was successfully transplanted to the Hiwassee River, where the population has risen to about 2,500 individuals. Another transplant attempt was made to the Nolichucky River in 1975, but was later stopped by the discovery of another federally protected species, the sharphead darter (Etheostoma acuticeps). Other unsuccessful transplant locations included lower parts of the Holston River, French Broad River, and middle Elk River. With the completion of the Tellico dam, the snail darter was extirpated from the Little Tennessee River. In 1980, additional populations of snail darters were discovered in South Chickamauga Creek in Chattanooga, the lower portion of Big Sewee Creek in Meigs County, the lower Sequatchie River in Marion County, Little River in Blount County, and the lower portion of Paint Rock River in Madison County, Alabama. These discoveries indicated the snail darter’s possible range as being from the lower reaches of major tributaries of the Tennessee River from the northward bend in Alabama upstream; the snail darter was reclassified from endangered to threatened in July 1984.
The snail darters are found in gravel shoals free of silt and aquatic plants, with moderate to strong currents, and moderate depths. The substrate generally consists of dark micaceous sand, with little to no silt, and 25 to 50 percent of the area scattered with gravel. Agricultural development has also affected the water clarity, and silt run-off causes problem for reproduction and migration. In 1976, the winter temperature ranged from 5° to 12°C, and summer temperature averaged near 18°C in the Little Tennessee River. These temperature fluctuations are due to impoundments, resulting in colder water when the dam is discharging and warming water when flow is diminished. Current velocities ranged from a moderate 0.25 m/s to nearly 0.7 m/s. The snail darter actively feeds in spring and winter with a diet consisting of 60% small gastropods (5mm or less in diameter) and other prey such as caddisflies, midges, and blackflies. Snails are the preferred food source until late spring when they outgrow the gape size of the fish, resulting in a diet change to insect larvae. The most effective predator on adult snail darters is Cottus carolinae while Salmo trutta, Morone chrysops, Sizostedion canadense, and other darters would prey on eggs and juveniles. The snail darters’ dorsal patterns and coloration allow the fish to camouflage with the substrate to avoid detection from predators. Burrowing behavior also is a defense mechanism and can help conserve energy for the current.
The snail darter spawning occurs in early February through April when water temperatures range from 12°-13°C. The female produces over 600 eggs and has multiple mates over the course of two weeks. The snail darter does not display territorial behavior during the breeding, unlike other species of darters. The eggs are deposited on the shallowest portion of gravel shoals and hatch after 15–20 days. Silt run-off can deprive eggs of oxygen, leading to higher mortality. When eggs hatch, the larvae drift downstream to deeper, calmer water and feed on zooplankton. The larvae are phototaxic (attracted to light) which may have implications regarding diurnal movements in the water column or depth maintenance. After 3 to 4 months of age, the juveniles migrate upstream during spring, and remain at the breeding shoal areas. The snail darter reaches sexual maturity at one year. The snail darter life span is 2 to 4 years, depending on predation and access to the breeding ground. More research on the snail darter life history is needed.
The snail darter is a federally protected species and is listed as threatened under the Endangered Species Act of 1973 as a result of habitat destruction from the completion of the Tellico Dam. Another factor in the decline of snail darters is siltation, which degrades spawning habitat and food availability. Other influences include agricultural development, environmental contamination and pollution, and channel modification, which affect the water clarity, reproduction success, and migration patterns. A recovery plan was made and completed on May 5, 1983.The recovery efforts focused on finding and transplanting individuals to suitable habitat areas in the Tennessee River, continuing research to locate already existing populations, and maintaining current populations of snail darters. Programs are in progress to educate the public and to work with state officials and local citizens to broaden protection efforts. However, more recent research on snail darters is still needed to better manage and protect the species and its habitat. The U.S. Fish and Wildlife Service, TVA, Tennessee Wildlife Resource Agency, and other law enforcement agencies are utilizing legislation and regulations to protect the snail darter during the recovery effort. It is recommended that at least five separate viable populations should be maintained, the species should be kept on the Federal List of Endangered and Threatened Wildlife, and Federal permits to collect the species should be required. As a result of the current recovery plan, the snail darter’s federal listing was degraded from endangered species to threatened species.
The snail darter is a threatened species and needs to be intensely managed to ensure the future of the species from possible extinction. The species must be monitored yearly, especially in the Hiwassee River, to determine what properties make the transplant successful. Locations where small populations of snail darter are in place should be monitored for invasive species and possible influences from rivers or tributaries that could alter the ecosystem dramatically. A possible management practice includes using seines nets and electroshocking to collect specimens to monitor population density annually in the transplant sites or in newly discovered pockets, such as South Chickamauga Creek. Specimen collection should be done during spawning in early February to mid-April for more accurate counts when individuals are more readily located. Another recommendation is protecting watersheds and river systems from pollution and siltation. Because snail darters prefer only substrate gravel, areas containing gravel should be protected from siltation from farming or construction activities to protect the breeding ground. Lastly, research should continue on the snail darter to gain more knowledge of its life history and distribution range of the species. If not for the efforts and actions of Etnier and Stiles during the debate of the completion of the Tellico Dam, the snail darter would be extinct.
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- Plater, Zygmunt (2013). The Snail Darter and the Dam: How Pork-Barrel Politics Endangered a Little Fish and Killed a River. Yale University Press. ISBN 0-300-17324-5.