Northern Riffleshell and Clubshell Reintroduction Project – Summary of Activities for 2017
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Native Freshwater Mussels
Native Freshwater Mussels Freshwater mussels, sometimes called clams, have always been and continue to be, an important food source for muskrat, minks, FACT SHEET raccoons, otters, fishes, and some birds such as herons. Historically, written by John Tautin Native Americans not only ate mussels but also used the shells for utensils, tools, and to make jewelry. Between the late 1800s and mid-1900s, shells were harvested to supply a multi- fluted shell million dollar pearl button industry. However, with the Lasmigona costata invention and widespread use of plastics during the 1940-50s, the pearl button industry collapsed. But by the 1950s the Japanese found a new use for mussel shells in cultured pearl production. e shells are cut and finished into beads and inserted into oysters to serve as nuclei for pearls. Still today, thousands of tons of mussel shells (especially Washboard, Mapleleaf, and ree-ridge mussels) are exported from the United States to Japan for this purpose. Elktoe Worldwide, there are about one thousand species of mussels. Mussels Alasmidonta marginata can be found on every continent but Antarctica. While the entire continent of Europe only has eight different species of mussels, there are twenty-five different species of mussels in French Creek, and about three-hundred in the United States. ese important animals are threatened, however. Today, over half of the species of mussel in the Midwest are threatened or endangered. In the French Creek watershed, thirteen species of mussels are listed as endan- gered or threatened in Pennsylvania. Four species (the northern riffleshell, kidney shell and clubshell, rayed bean, and snuffbox) are endangered at the federal level. -
Pleurobema Clava Lamarck Northern Northern Clubshell Clubshell, Page 1
Pleurobema clava Lamarck Northern Northern Clubshell Clubshell, Page 1 State Distribution Photograph courtesy of Kevin S.Cummings, Illinois Natural History Survey Best Survey Period Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Status: State and Federally listed as Endangered umbos located close to the anterior end of the shell. Viewed from the top, the clubshell is wedge-shaped Global and state ranks: G2/S1 tapering towards the posterior end. Maximum length is approximately 3 ½ inches (90mm). The shell is tan/ Family: Unionidae (Pearly mussels) yellow, with broad, dark green rays that are almost always present and are interrupted at the growth rings. Total range: Historically, the clubshell was present in There is often a crease or groove near the center of the the Wabash, Ohio, Kanawha, Kentucky, Green, shell running perpendicular to the annular growth rings. Monogahela, and Alleghany Rivers and their tributaries. Beak sculpture consists of a few small bumps or loops, Its range covered an area from Michigan south to or is absent. Alabama, and Illinois east to Pennsylvania. The The clubshell has well-developed lateral and pseudo- clubshell currently occurs in 12 streams within the cardinal teeth and a white nacre. Shells of males and Tennessee, Cumberland, Lake Erie, and Ohio drainages. females are morphologically similar. Similar species These include the St. Joseph River in Michigan (Badra found in Michigan include the kidneyshell and Goforth 2001) and Ohio (Watters 1988), (Ptychobranchus fasciolaris) which is much more Pymatuning Creek (Ohio)(Huehner and Corr 1994), compressed laterally than the clubshell and has a kidney Little Darby Creek (Ohio), Fish Creek (Ohio and shaped outline; the round pigtoe (Pleurobema sintoxia) Indiana), Tippecanoe River (Indiana), French Creek which has a more circular outline and does not have (Pennsylvania), and the Elk River (West Virginia). -
Appendix K-1 – Endangered Species Habitat and Wildlife Technical Report
I-69 Ohio River Crossing Project Draft Environmental Impact Statement APPENDIX K-1 Endangered, Threatened, and Rare Species Habitat Assessment and Wildlife Technical Report Clarification Note for Central Alternative 1: Central Alternatives 1A and 1B as described in the DEIS are physically the same alternative. The only difference between them is that Central Alternative 1A would include tolls on both the new I-69 bridge and on the US 41 bridge. Central Alternative 1B would only include tolls on the new I-69 bridge. Any reference in this document to Central Alternative 1 applies to both Central Alternative 1A and Central Alternative 1B. Appendices October 15 , 2018 (1'$1*(5('7+5($7(1(' $1'5$5(63(&,(6+$%,7$7 $66(660(17 $1':,/'/,)( 7( CHNICAL 5(3257 I-69I-69 O OHIOHI O RRIVERIVER CCROSSINGROSS IN G PPROJECTROJ ECT Evansville, IN and Henderson, KY I N D O T Endangered, Threatened, and Rare Species Habitat Assessment and Wildlife Technical Report I-69 Ohio River Crossing Project Evansville, IN and Henderson, KY Prepared by: Stantec Consulting Services I-69 Ohio River Crossing Project ETR Species Habitat Assessment and Wildlife Technical Report TABLE OF CONTENTS CHAPTER 1 – INTRODUCTION ............................................................................. 1-1 West Alternative 1 ............................................................................................. 1-4 West Alternative 2 ............................................................................................. 1-6 Central Alternative 1 ....................................................................................... -
Epioblasma Torulosa Rangiana (Lea) Northern Riffleshell
Epioblasma torulosa rangiana (Lea) Northern Riffleshell State Distribution Photo by Kevin Cummins, courtesy of the Illinois Natural History Survey Best Survey Period Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Status: Federal and state endangered able sexual dimorphism in riffleshells. Male shells have a sulcus, or ridge, running posterio-ventrally from just Global and State Rank: G2T2/S1 below the beak. Female shells have a low bulge along the posterio-ventral edge of the shell that accommodates Family: Unionidae (Pearly Mussels) the enlarged marsupium containing eggs. Total Range: The northern riffleshell was found Best Survey Time: April through June. historically in Illinois, Indiana, Kentucky, Michigan, Ohio, Pennsylvania, West Virginia, and western Habitat: The northern riffleshell requires swiftly Ontario. It was widespread in the Ohio and Maumee moving, well-oxygenated water. Riffle and run areas River basins, and in tributaries of western Lake Erie. with fine to coarse gravel are the preferred habitats. Today, the northern riffleshell occurs in short reaches of the Green River in Kentucky; the Detroit and Black Biology: The northern riffleshell has been observed to Rivers in Michigan; Big Darby Creek in Ohio; and be gravid from late summer to the following spring, at French Creek, LeBoeuf Creek and the Allegheny River which time the glochidia are released (Ortmann 1912, in Pennsylvania (Stansberry et al. 1982). Clarke 1987). The females use the posterior portion of the outer gill as a brood pouch, or marsupium, that is State Distribution: The range of the northern riffleshell accomodated by the swelling of the female shell. in Michigan is restricted to the eastern border of the Under laboratory conditions, glochidia developed with state. -
Delisting Targets for Fish/Wildlife Habitat & Population Beneficial Use Impairments for the Clinton River Area
DELISTING TARGETS FOR FISH/WILDLIFE HABITAT & POPULATION BENEFICIAL USE IMPAIRMENTS FOR THE CLINTON RIVER AREA OF CONCERN Submitted to the Michigan Department of Environmental Quality May 8, 2009 Submitted by: 2200 Commonwealth Blvd, Suite 300 Ann Arbor, MI 48105 Ph: 734-769-3004 Fax: 734-769-3164 ACKNOWLEDGMENTS We would like to acknowledge the United States Environmental Protection Agency (EPA)’s Great Lakes National Program Office (GLNPO) for funding the final phase of this project. At GLNPO, thanks are due to Mr. Tony Kizlauskas (Contract Manager), Ms. Vicki Thomas, and Mr. Mark Elster (both Senior Advisors) for facilitating various administrative components of this project. The first phase of this project was conceived amongst Clinton River Public Advisor Council’s Chairman Mark Richardson, Clinton River Watershed Council’s (CRWC) past Executive Director Jessica Pitelka Opfer, Environmental Consulting & Technology Inc. (ECT) Senior Program Manager Roy Schrameck, and ECT’s Vice President Sanjiv Sinha. Having preceded the development of state-wide targets in Michigan and parallel to efforts in only couple other Areas of Concerns (AOCs), that project was a precursor to many similar efforts across the Great Lakes basin. Many experts contributed their time, efforts, and talent toward the preparation of this report. The Project Team acknowledges the contributions of each of the following members of the Clinton River AOC Delisting Targets Technical Committee, and thanks them for their efforts: Dr. David Allan, University of Michigan Mrs. Laura Evans, U.S. Environmental Protection Agency Mrs. Donna Folland, Oakland Land Conservancy Mr. James Francis, Michigan Dept of Natural Resources Dr. Carl Freeman, Wayne State University Ms. -
Recovery Strategy for Northern Riffleshell (Epioblasma Torulosa
PROPOSED Species at Risk Act Recovery Strategy Series Recovery Strategy for Northern Riffleshell, Snuffbox, Round Pigtoe, Mudpuppy Mussel and Rayed Bean in Canada August 2006 About the Species at Risk Act Recovery Strategy Series What is the Species at Risk Act (SARA)? SARA is the Act developed by the federal government as a key contribution to the common national effort to protect and conserve species at risk in Canada. SARA came into force in 2003 and one of its purposes is “to provide for the recovery of wildlife species that are extirpated, endangered or threatened as a result of human activity.” What is recovery? In the context of species at risk conservation, recovery is the process by which the decline of an endangered, threatened or extirpated species is arrested or reversed, and threats are removed or reduced to improve the likelihood of the species’ persistence in the wild. A species will be considered recovered when its long-term persistence in the wild has been secured. What is a recovery strategy? A recovery strategy is a planning document that identifies what needs to be done to arrest or reverse the decline of a species. It sets goals and objectives and identifies the main areas of activities to be undertaken. Detailed planning is done at the action plan stage. Recovery strategy development is a commitment of all provinces and territories and of three federal agencies — Environment Canada, Parks Canada Agency and Fisheries and Oceans Canada — under the Accord for the Protection of Species at Risk. Sections 37–46 of SARA (http://www.sararegistry.gc.ca/the_act/default_e.cfm) spell out both the required content and the process for developing recovery strategies published in this series. -
Final Biological Opinion Re: EPA Final Rule
United States Department of the Interior FISH AND WILDLIFE SERVICE Washington, D.C. 20240 In Response Refer To: FWS/ AES/DERIBCH/OS6 189 Mr. Robert Wood Director Engineering and Analysis Division Office of Water U.S. Environmental Protection Agency Washington, D.C. 20460 Dear Mr. Wood: In accordance with section 7 of the Endangered Species Act (ESA) of 1973, as amended (16 U.S.C. 1531 et seq.), and the Interagency Cooperation Regulations (50 CFR 402), this transmits our final biological opinion (Opinion) on the U.S. Environmental Protection Agency's (EPA) issuance and implementation of the final regulations implementing Section 316(b) of the Clean Water Act (CWA). Section 7(a)(2) ofthe ESA of1973, as amended (16 U.S.C. 1536(a)(2)), requires Federal agencies to insure that any action they authorize, fund, or carry out is not likely to jeopardize the continued existence of any endangered or threatened species or result in the destruction or adverse modification of critical habitat. When a Federal agency's action may affect listed species or critical habitat, formal consultation with the National Marine Fisheries Service (NMFS) and/or the U.S. Fish and Wildlife Service (USFWS) is required (50 CFR 402.14(a)). EPA requested formal consultation even though EPA was ofthe opinion that its action would not cause adverse effects to listed species and critical habitat. After review of the proposed regulation, biological evaluation, and other available information we determined that the proposed action is likely to adversely affect threatened and endangered species and designated critical habitat. Federal agencies may request a conference on a proposed action that may affect proposed species or proposed critical habitat. -
Mussels Only)
MUSSEL CWCS SPECIES (46 SPECIES) Common name Scientific name Bleufer Potamilus purpuratus Butterfly Ellipsaria lineolata Catspaw Epioblasma obliquata obliquata Clubshell Pleurobema clava Cracking Pearlymussel Hemistena lata Creek Heelsplitter Lasmigona compressa Cumberland Bean Villosa trabalis Cumberland Elktoe Alasmidonta atropurpurea Cumberland Moccasinshell Medionidus conradicus Cumberland Papershell Anodontoides denigratus Cumberlandian Combshell Epioblasma brevidens Dromedary Pearlymussel Dromus dromas Elephantear Elliptio crassidens Elktoe Alasmidonta marginata Fanshell Cyprogenia stegaria Fat Pocketbook Potamilus capax Fluted Kidneyshell Ptychobranchus subtentum Green Floater Lasmigona subviridis Kentucky Creekshell Villosa ortmanni Little Spectaclecase Villosa lienosa Littlewing Pearlymussel Pegias fabula Longsolid Fusconaia subrotunda Mountain Creekshell Villosa vanuxemensis vanuxemensis Northern Riffleshell Epioblasma torulosa rangiana Orangefoot Pimpleback Plethobasus cooperianus Oyster Mussel Epioblasma capsaeformis Pink Mucket Lampsilis abrupta Pocketbook Lampsilis ovata Purple Lilliput Toxolasma lividus Pyramid Pigtoe Pleurobema rubrum Rabbitsfoot Quadrula cylindrica cylindrica Rayed Bean Villosa fabalis Ring Pink Obovaria retusa Rough Pigtoe Pleurobema plenum Round Hickorynut Obovaria subrotunda Salamander Mussel Simpsonaias ambigua Scaleshell Leptodea leptodon Sheepnose Plethobasus cyphyus Slabside Pearlymussel Lexingtonia dolabelloides Slippershell Mussel Alasmidonta viridis Snuffbox Epioblasma triquetra Spectaclecase -
Morphometric Analyses Distinguish Wabash Pigtoe (Fusconaia Flava
diversity Article Morphometric Analyses Distinguish Wabash Pigtoe (Fusconaia flava) and Round Pigtoe (Pleurobema sintoxia) Mussels Julia A. Willsie 1, Todd J. Morris 2 and David T. Zanatta 1,3,* 1 Department of Biology, Central Michigan University, Mt. Pleasant, MI 48859, USA; [email protected] 2 Fisheries and Oceans Canada, Great Lakes Laboratory for Fisheries and Aquatic Sciences, 867 Lakeshore Rd., Burlington, ON L7S 1A1, Canada; [email protected] 3 Institute for Great Lakes Research, Central Michigan University, Mt. Pleasant, MI 48859, USA * Correspondence: [email protected] Received: 24 June 2020; Accepted: 31 August 2020; Published: 3 September 2020 Abstract: Wabash Pigtoe, Fusconaia flava, and the related Round Pigtoe, Pleurobema sintoxia, are freshwater mussels (Bivalvia: Unionidae: Pleurobemini) native to the Great Lakes region of North America. Fusconaia flava is considered widespread and relatively common while P. sintoxia is considered an imperiled species. These species are similar in shell shape and coloration and have confounded many freshwater malacologists, resulting in frequent misidentifications. We sought to determine if morphometric analyses could be used to reliably distinguish between these species. Two hundred and forty-six specimens were collected from rivers in Michigan and Ontario. For each specimen, a preliminary identification was made, shell measurements and foot color (orange or white) were documented, and photos of the left shell valve were taken. A genetic sample was taken from 133 specimens for cytochrome c oxidase subunit 1 (COI) barcoding. COI sequences were used for species identification by comparing to sequences on GenBank. Twenty-one digitized landmarks along the outline of the left valve were analyzed and compared to the results of the DNA barcoding. -
The Purple Wartyback Mussel (Bivalvia: Unionidae), in the Olentangy River, Delaware County, Ohio
44 PURPLE WARTYBACK MUSSEL IN OLENTANGY RIVER VOL. 108 BRIEF NOTE Discovery of a Population of Cyclonaias tuberculata (Rafinesque), the Purple Wartyback Mussel (Bivalvia: Unionidae), in the Olentangy River, Delaware County, Ohio Michael J. Bolton1, Division of Surface Water, Ohio EPA, 4675 Homer Ohio Lane, Groveport, OH Abstract. Freshwater mussels (Unionidae) were collected from the Olentangy River upstream from the city of Delaware, Delaware County, Ohio to verify the existence of a population of Cyclonaias tuberculata (Rafinesque), the Purple Wartyback Mussel. Eleven live specimens of C. tuberculata were found, including two juveniles, in the second and third riffle complexes downstream from the Panhandle Road dam (40°19’21.03”N, 83°4’13.68”W). This is the first time that this species has been found alive in the Olentangy River basin since the 1800s. OHIO J SCI 108 (3) 44-46, 2008 INTRODUCTION MATERIALS AND METHODS There are 80 species or subspecies of freshwater mussels (Bivalvia: After an initial discovery on 15 June 2007 of what was believed Unionoida: Margaritiferidae, Unionidae) thought to be indigenous to be a specimen of C. tuberculata from the Olentangy River, a to Ohio, of which five are considered to be extinct, 14 extirpated, more thorough search of the area was initiated. Freshwater mussels 24 endangered, four threatened, and nine species of concern were searched for by visually scanning the stream substrates for (Watters 1995, ODNR 2007). Cyclonaias tuberculata (Rafinesque), live and dead shells and the stream banks for dead shells. Water the Purple Wartyback Mussel, is widely distributed in Ohio and clarity was low on every visit with an effective viewing depth of found in clean streams and rivers. -
Recovery Strategy for the Northern Riffleshell, Snuffbox, Round Pigtoe, Mudpuppy Mussel and Rayed Bean in Ontario
Photo: Environment Canada Northern Riffleshell (Epioblasma torulosa rangiana) in Ontario Snuffbox (Epioblasma triquetra) in Ontario Round Pigtoe (Pleurobema sintoxia) in Ontario Mudpuppy Mussel (Simpsonaias ambigua) in Ontario Rayed Bean (Villosa fabalis) in Ontario Ontario Recovery Strategy Series Recovery strategy prepared under the Endangered Species Act, 2007 September 2010 Ministry of Natural Resources About the Ontario Recovery Strategy Series This series presents the collection of recovery strategies that are prepared or adopted as advice to the Province of Ontario on the recommended approach to recover species at risk. The Province ensures the preparation of recovery strategies to meet its commitments to recover species at risk under the Endangered Species Act, 2007 (ESA, 2007) and the Accord for the Protection of Species at Risk in Canada. What is recovery? What’s next? Recovery of species at risk is the process by which the Nine months after the completion of a recovery strategy decline of an endangered, threatened, or extirpated a government response statement will be published species is arrested or reversed, and threats are which summarizes the actions that the Government of removed or reduced to improve the likelihood of a Ontario intends to take in response to the strategy. The species’ persistence in the wild. implementation of recovery strategies depends on the continued cooperation and actions of government agencies, individuals, communities, land users, and What is a recovery strategy? conservationists. Under the ESA, 2007, a recovery strategy provides the best available scientific knowledge on what is required For more information to achieve recovery of a species. A recovery strategy outlines the habitat needs and the threats to the To learn more about species at risk recovery in Ontario, survival and recovery of the species. -
Us and Life History of the Three Assessed Mussels
Appendix C: Status and Life History of the Three Assessed Mussels August 29, 2007 Appendix C: Status and Life History of the Three Assessed Mussels General information on the habitat requirements, food habits, growth and longevity, reproduction, and past and current threats of the assessed mussels is provided below in Section C.1. Species-specific information for the following three assessed mussels is provided in Sections C.2 through C.4: • Fat pocketbook pearly mussel • Purple cat’s paw pearly mussel • Northern riffleshell C.1 General Information C.1.1 Habitat Adult mussels are usually found in localized stream patches (beds) almost completely burrowed in the substrate with only the area around the siphons exposed (Balfour and Smock, 1995). The composition and abundance of mussels are directly linked to bed sediment distributions (Neves and Widlak, 1987; Leff et al., 1990), and physical qualities of the sediments (e.g., texture, particle size) may be important in allowing the mussels to firmly burrow in the substrate (Lewis and Riebel, 1984). In addition, other aspects of substrate composition, including bulk density (mass/volume), porosity (ratio of void space to volume), sediment sorting, and the percentage of fine sediments, may also influence mussel densities (Brim Box, 1999; Brim Box and Mossa, 1999). According to Huehner (1987), water velocity may be a better predictor than substrate for determining where certain mussel species are found in streams. In general, heavy-shelled species occur in stream channels with stronger currents, while thin-shelled species occur in more backwater areas. Stream geomorphic and substrate stability is especially crucial for the maintenance of diverse, viable mussel beds (Vannote and Minshall, 1982; Hartfield, 1993; Di Maio and Corkum, 1995).