Barrens topminnow

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Barrens topminnow
Scientific classification
Kingdom: Animalia
Phylum: Chordata
Class: Actinopterygii
Order: Cyprinodontiformes
Family: Fundulidae
Genus: Fundulus
Species: F. julisia
Binomial name
Fundulus julisia
J. D. Williams & Etnier, 1982

The Barrens topminnow (Fundulus julisia) is a species of freshwater fish in the Fundulidae family,[2] which is in need of management so that it may continue to and increasingly survive in the wild. There are many potential causes of decline of this species including the invasive western mosquitofish (Gambusia affinis) that will replace native species on a population level, wadding piscivorous birds preying on adults, and the overall restricted distribution of the species.[3] Managing for this species is vital for its success, but to do so there must be an understanding of the species' characteristics. It is endemic to a small portion of Tennessee in the Elk River and the West Hickory creek of the Cumberland river drainage.[4] living up to only 3 years the life span of F. julisia is very short. In many cases the majority of the population does not even reach that age.[5] Most adult males are eaten by birds because of their bright coloration during breeding season.[4] Current management plans are in place for the improvement of the species such as captive breeding and reintroduction, and also private management of streams and land. Yet, more can be done to aid them in their survival efforts. Buffer zones around streams can be created to promote the health of the stream and close observation of the introduced populations needs to be a priority. With only three small original populations left in the wild[6] it is important that species survive in captivity, but more so in its natural environment.

Geographic Distribution of Species[edit]

F. julisia is not only found in one state, Tennessee, but also in only one region, the Cumberland Plateau. In that specific region it is currently only found in the Elk River and a drainage creek of the Cumberland River, West Hickory Creek.[4] However, that has not always been the only thought of location for F. julisia's habitat. They are often associated with springs, but drought conditions made them adapt to survive in springs where permanent water was near by. They prefer heavily vegetated areas of aquatic vegetation or algae in shallow, slow moving water.[7] Given the above habitat, it is observed that F. julisia can tolerate warm temperatures of water and turbidity, the presence of competitors, and the presence of predators. This, along with spawning, make aquatic vegetation a limiting factor for the fish.[8]

Ecology[edit]

In overall behavior F. julisia does not differ greatly from other members of the Fundulus genus. It is an opportunistic carnivore that preys upon crustaceans, gastropods (snails and slugs), and insects that are both aquatic and that fall into the substrate.[7] In an examination of gut contents it was found that crustaceans made up 64% of their diet while aquatic insects made up 23% and various other organisms made up the remaining 13%.[3] It competes for this prey with Fundulus catenatus (Northern studfish)and Gambusia affinis (Western mosquitofish). This is an interesting relationship because G. affinis is one of the leading causes of decline in F. julisia due to competition for the same prey.[9] F. julisia is preyed upon by bass (Micropterus species) and sunfish (Lepomis species) within the substrate. Outside the water F. julisia is preyed upon by piscivorous birds that spear them with a sharp tipped beak or catch them with ridged edged beaks.[3] During breeding season males are easily spotted due to their bright mating colors, which makes them easier prey. Males have been found to have two different morphs with the primary difference being the marginal and submarginal bands on the caudal and posterior dorsal fin. One morph has a pale yellow submarginal band and the other translucent blue with white and orange submarginal band.[10] All females are far less colorful appearing yellowish and washed out. Even as juveniles males and females can be distinguished from one another due to the males having an iridescent green coloration on their sides.[10]

Life History[edit]

Breeding season for this species is annual and is believed to be as early as mid-March when the males were observed to first have their breeding colors. At this time the water temperature is roughly 14-15 C. Eggs have been collected in mid-April from clumps of algae. Females lay around 200-250 mature ova over a period time, laying only a few daily.[10] Though relatively opportunistic in spawning sites, F. julisia egg morphology suggests that submergent vegetation is most preferred and in turn most successful. Loss of successful spawning sites could be one of the main ecological factors that limit its distribution.[10] Territoriality has been observed in the field, but it is more abundant in aquaria settings. In aquaria males have been observed defending portions of the tank that resulted in a single male's dominance. In the field males only slightly defend their clumps of filamentous algae. Females never exhibited territorial behavior in the field, but were seen defending feeding areas in the aquaria. Sexual maturity is reached at 1 year with a maximum lifespan of 3 years, though most individuals do not live that long and die off after spawning.[10]

Current Management[edit]

Currently there is not a tremendous amount of physical work being put into the protection of F. julisia. There are however organizations that realize something needs to be done in order to protect and preserve this species. The Nature Conservancy of Tennessee (TNC) is working with private landowners to preserve local habitats known to support F. julisia. The Tennessee Wildlife Resources Agency (TWRA) is also participating in these activities and upgraded the state status of the species to endangered. The U.S. Fish and Wildlife Service (USFWS) and the Natural Resources Conservation Service (NRCS) are also actively funding and assisting landowners to protect habitat, both where the fish currently occurs, as well as at sites where populations are currently being or may be restored in the near future.[8] Through the aid of these organizations captive breeding programs have been successful and reintroduction to areas of the Barrens Plateau are under current operation.[4]

Management Recommendations[edit]

In relation to current management plans it is important to continue monitoring the introduced populations for success, failure, and any other occurrence such as over predation and lack of viable habitat. Land management should also be incorporated into F. julisia's management. The success of the stream is directly related to the success of the land. Buffer zones need to be put in to protect the stream habitats from runoff and siltation. These zones need to be at least 20–35 feet wide extending outward from the stream to add stability to the tree species and prevent blow down into water.[11] Canopy cover from trees will moderate temperature and create woody debris in the substrate that will create micro-habitats that support prey species of F. julisia. This will also deter access to the stream, thus maintaining its health. Open water habitats that are shallow and slow moving need to be created along with the addition and growth of filamentous algae for success in spawning.[4] To ensure the population is stabilized, periodic sampling is highly recommended. Sampling should occur at least every 6 months to monitor breeding and survival success rates. Electroshockers would be the most accurate way to find a population size. It allows you to catch a larger batch of fish and gives you time to examine and take measurements while the fish is stunned. Shocking should take place in the pool portions of the streams leading up to the riffle area since F. julisia is known to attempt to escape from predators in that portion of the stream. Evasive species should be monitored and removed if they become a threat to the livelihood of F. julisia. This should also be done via electroshocking. With these management practices in place F. julisia populations should be able to be maintained and even increased over time.

References[edit]

  1. ^ NatureServe (2013). "Fundulus julisia". The IUCN Red List of Threatened Species. IUCN. 2013: e.T8707A18229539. doi:10.2305/IUCN.UK.2013-1.RLTS.T8707A18229539.en. Retrieved 9 November 2017. 
  2. ^ Gimenez Dixon, M. 1996. Fundulus julisia. 2006 IUCN Red List of Threatened Species. Archived June 27, 2014, at the Wayback Machine. Downloaded on 4 August 2007.
  3. ^ a b c Laha, M. And Mattingly, H. T. 2006. Identifying environmental conditions to promote species coexistance: an example with the native Barrens topminnow and invasive Western mosquitofish (Gambusia affinis) . Biological invasions. 8” 719-725.
  4. ^ a b c d e Johnson, A. B. And Bettoli, P. W. 2003. Threatened fishes of the world: Fundulus Jullisa Williams & Etnier, 1982 (Cyprinodontidae). Environmental Biology of Fishes 68: 240-240
  5. ^ Goldsworthy, C. A. And Bettoli, P.W. 2006. Growth, body condition, reproduction and survival of stocked Barrens Topminnows, Fundulus julisia (Fundulidae). American Midland Naturalist. 156(2): 331-343.
  6. ^ http://conservationfisheries.org/index.php/species/current-species/fundulus-julisia-barrens-topminnow/
  7. ^ a b Etnier, D. A. 1983. Status report for Barrens topminnow (Fundulus julisia Williams and Etnier). Publ. of Tenn. Wildlife Resources Agency, Nashville, TN 37204. PCAN No. 0064.
  8. ^ a b Rakes, P.L. And U.S. Fish and Wildlife Service. 2003. Survey of selected historic sites, potential new localities, and restoration sites for the Barrens topminnow, Fundulus julisia, on the Barrens Plateau of middle Tennessee.
  9. ^ Laha, M. And Mattingly, H. T. 2007. Ex situ evaluation of impacts of invasive mosquitofish on the imperiled Barrens topminnow. 78(1) 1-11.
  10. ^ a b c d e Rakes, P. L. Life History and Ecology of the Barrens Topminnow, Fundulus Julisia Williams and Ethier (Pisces, Fundulidae). M.S. Thesis, The University of Tennessee. 64 pp.
  11. ^ http://www.epa.gov/owow/NPS/MMGI/Chapter3/ch3-2b.html