Greater redhorse | |
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Greater Redhorse (Moxostoma valenciennesi) | |
Scientific classification ![]() | |
Domain: | Eukaryota |
Kingdom: | Animalia |
Phylum: | Chordata |
Class: | Actinopterygii |
Order: | Cypriniformes |
Family: | Catostomidae |
Genus: | Moxostoma |
Species: | M. valenciennesi
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Binomial name | |
Moxostoma valenciennesi (D. S. Jordan, 1885)
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Synonyms | |
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![The distribution of the Greater Redhorse extends latitudinally from southeastern North Dakota to eastern New York and longitudinally from northern Michigan to southern Ohio.](/wikipedia/commons/thumb/d/de/Greater_Redhorse.jpg/220px-Greater_Redhorse.jpg)
The greater redhorse (Moxostoma valenciennesi) is a species of freshwater fish found in northeastern North America. It is the largest member of the genus Moxostoma, with a maximum length of 80 cm (31.5 in). The greater redhorse is long lived with a maximum reported age of 27 years.[2]
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Recovering the Robust Redhorse
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River Redhorse Sucker Spawning
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Golden Redhorse Suckers Spawning
Transcription
Well we were conducting a fishery survey on the Oconee River in 1991 for the relicensing of Sinclair Dam when we collected these five large fish, members of the sucker family that we could not identify so we contacted some local experts on this group of fish and conducted an investigation and pieced together gradually over a period of couple of years exactly what this fish was. Well it turns out that the robust redhorse was actually initially described by the naturalist Edward Cope in 1869 from the Atkin River in North Carolina and then essentially disappeared from the scientific record for over 100 years until these fish from the Oconee River led to its rediscovery and really the beginning of this now 20-year recovery effort. Georgia Power became involved with robust redhorse because the fish was actually discovered in the Oconee River below one of our hydro plants during a relicensing project. So from a dam owner perspective, that can be a little interesting. All of a sudden this fish species that nobody's seen for 100 years, that may in fact be in jeopardy is now in our tailrace and ultimately affects the way that we operate. So Georgia Power's been involved since the very beginning. The U.S. Fish and Wildlife Service, Georgia Department of Natural Resources and Georgia Power collaboratively developed an agreement called a Candidate Conservation Agreement with Assurances or CCAA to aid in the recovery of the robust redhorse. Broadly speaking, CCAAs are one tool in our tool box that we can collectively use to recover these at-risk species. CCAAs are a prelisting recovery approach, meaning that the Service works with our non-federal partners to conserve these at-risk species before they are listed under the Endangered Species Act. Specifically speaking for the Robust Redhorse CCAA, we had two main objectives. The first objective was to establish a new population within the historic range of the species, and that's where we are today, the Ocmulgee River, Georgia, and the second objective was to contribute to the understanding of the habitat use and life history requirements of the fish. When the robust redhorse was first discovered, it qualified for listing, but because of the urgency of the need for conservation, a prelisting recovery approach was decided as the course of action. We've gone from one population to six populations, and those populations seem to be in really good shape, so the need for listing is much less now than when we found the animal initially. The candidate conservation agreement is a good vehicle for formalizing the work to be done in any conservation action. In this particular case, we had a very large group of partners and stakeholders each doing various conservation measures. Like all species, the robust redhorse is the legacy of millions of years of evolution, and struggle that would be a tragedy to lose. We cannot afford to lose any more species. I mean, if our ecosystems can't support a diversity of species the n at some point maybe at some point they would not be able to support us. The question that we're often asked is was it worth it, was it worth engaging in this and putting forth a lot of effort and a lot of money up front in order to ultimately or hopefully protect the species? Well the reality is from a business perspective yes, because there's a lot more risk in uncertainty in the future than there is in knowing what your costs are. So while we may spend thousands of dollars on conservation activities now, it's a lot less risky than finding out 10 years down the road that we have a significant endangered species issue that could be costly orders of magnitude greater than what we've spent already so definitely from a business perspective dealing with the known is much cheaper than dealing with the unknown.
Distribution and habitat
The greater redhorse is endemic to states in the northcentral and northeastern United States as well as Ontario and Quebec in Canada. It is typically found in clear, relatively fast-moving rivers and in both shallow and deep waters in some lakes. They are unable to survive in even the slightest polluted waters. They, therefore have the ability to detect contaminated water sources.
Description
The greater redhorse is the largest fish in its genus, averaging around 46 cm (18 in) and 2 kg (4.4 lb), and reaching a maximum size of 80 cm (31.5 in) and 5.9 kg (13 lb). This species of fish has small eye sockets in contrast to their large rounded skull. On either side of the greater redhorse's body are reddish gold pectoral fins and pelvic fins. The posterior part of the dorsal fin varies from slightly concave at youth to slightly convex in adulthood. Their tail fins are only slightly notched, a trait that usually evolved in slow swimming bottom-feeders. The greater redhorse is most easily identified by its bright rusty red colored tail fin and the rows of black spots along its sides and back.
Diet habits
A bottom-feeder's mouth opens in the inferior position of the ventral surface of the fish. It feeds on various bottom dwelling organisms including, microcrustaceans, aquatic and larval insects, detritus, snails, and algae.
Reproduction and life cycle
Spawning for the greater redhorse begins in May or June.[3] Before they are able to build their gravel and sand nests, they locate an area in moderately fast waters. Once male territories are established, the females will visit two males at a time and begin their spawning process. The two males will surround the female and perform a shaking motion releasing both the sperm and eggs from said gendered fish. Upon burial of the eggs, the parents leave with no further parental care provided. Following fertilization, the greater redhorse eggs will hatch six to eight days at a mean temperature of 19 °C. Growth rates of this species are controversial among various areas they inhabit. The greater redhorse takes several years to reach sexual maturity and frequently attain ages more than 20 years, making them one of the longer-lived redhorse species.[2]
Relationship with humans
Overall, the greater redhorse is being threatened across its range. Although once not a popular sporting fish, this long-lived and late-maturing species is now subject to unregulated bowfishing, where tons of fish are shot for sport with no use of the fish afterwards and hauls exceed that of the commercial harvest by 200 times.[2] Thus, the greater redhorse is in dire need of conservation and management, especially with respect to wanton waste of bowfishing. The greater redhorse's status as a prey species is integral to the ecosystems to which they are native. Because this species is impacted greatly by pollutants, their endangered status may come from a decreased conscientiousness of where wastes are disposed of. The IGFA world record for the species stands at 12lb 7oz caught from the Sauk River near Melrose, Minnesota in 2005.[4] The greater redhorse is also being increasingly pursued by rod-and-line anglers of the 21st Century.[5][6]
References
- ^ NatureServe (2014). "Moxostoma valenciennesi". IUCN Red List of Threatened Species. 2014: e.T202259A18228653. doi:10.2305/IUCN.UK.2014-3.RLTS.T202259A18228653.en. Retrieved 11 November 2021.
- ^ a b c Lackmann, Alec R.; Bielak-Lackmann, Ewelina S.; Jacobson, Reed I.; Andrews, Allen H.; Butler, Malcolm G.; Clark, Mark E. (2023-08-30). "Harvest trends, growth and longevity, and population dynamics reveal traditional assumptions for redhorse (Moxostoma spp.) management in Minnesota are not supported". Environmental Biology of Fishes. doi:10.1007/s10641-023-01460-8. ISSN 1573-5133.
- ^ Reid, S. M. (June 2006). "Timing and Demographic Characteristics of Redhorse Spawning Runs in Three Great Lakes Basin Rivers". Journal of Freshwater Ecology. 21 (2): 249–258. doi:10.1080/02705060.2006.9664993. ISSN 0270-5060.
- ^ "Greater, redhorse". igfa.org. International Game Fish Association. Retrieved 17 May 2019.
- ^ Winter, Tyler. "Trash Fish Tuesday: Redhorse". www.themeateater.com. Retrieved 2023-09-04.
- ^ "Redhorse river: Fishing for St. Croix suckers offers serious sport". St. Croix 360. 2020-05-14. Retrieved 2023-09-04.
- "Moxostoma valenciennesi". Integrated Taxonomic Information System. Retrieved 6 June 2006.
- Froese, Rainer; Pauly, Daniel (eds.) (2005). "Moxostoma valenciennesi" in FishBase. November 2005 version.
- Fishes of Wisconsin. The University of Wisconsin Press. 1983. ISBN 0-299-08790-5.
- Ohio DNR - Moxostoma valenciennesi
- Wisconsin DNR - Moxostoma valenciennesi
- U.S. Geological Survey - Moxostoma valenciennesi
- NatureServe - Moxostoma valenciennesi
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