Recovery Strategy for Northern Riffleshell (Epioblasma Torulosa
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Recovery Strategy for Northern Riffleshell, Snuffbox, Round Pigtoe, Mudpuppy Mussel and Rayed Bean in Canada
Recovery Strategy for Five Ontario Freshwater Mussels December 2006 Species at Risk Act Recovery Strategy Series Recovery Strategy for Northern Riffleshell, Snuffbox, Round Pigtoe, Mudpuppy Mussel and Rayed Bean in Canada. December 2006 Recovery Strategy for Five Ontario Freshwater Mussels December 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. -
Tennessee's Extinct Species
Tennessee's Extinct Species The following species Birds: once occurred in Carolina parakeet Conuropsis carolinensis Ectopistes migratorius Tennessee and are now Passenger pigeon believed to be extinct. Mammals: Following this list are two Eastern elk species descriptions-one Fishes: describing the Carolina Harelip sucker parakeet and another describing the extinct Mussels: Acornshell Epioblasma haysiana freshwater mussels Angled riffleshell Epioblasma biemarginata of Tennessee. Cumberland leafshell Epioblasma stewardsoni Leafshell Epioblasma flexuosa Narrowcat's paw Epioblasma lenoir Rough rockshell Quadrula tuberosa Round combshell Epioblasma personata Sugarspoon Epioblasma arcaeformis Tennessee riffleshell Epioblasma propinqua Carolina Parakeet Status Habitat The Carolina parakeet is an The Carolina parakeet was found Learn rrwreabout extinct species. in riverine forests, cypress swamps, Tennessee's diverse and other woodlands over much of Description the Eastern and Midwest Regions of ecosyster.n3.Su~ort The Carolina parakeet was a the United States. It was the only conservation in your small parrot, about 12inches in parrot native to the United States. community and state! length. Its head was lemon yellow, The parakeets rested at night in with an orange forehead and cheeks. groups, with as many as 30 birds The rest of its body was green. Its sleeping inside one hollowtree, while legs and beak were pale pinkish- others would hang on the outside. white. These curious birds lived and Nests were placed in hollowtrees, traveled in flocks. and three to five white eggs were laid. Up to 50 nests were often crowded into one tree. Role in the Ecosystem Carolina parakeets enjoyed a variety of different foods-apples, peaches, mulberries, pecans, grapes, dogwood fruit, and grains. -
Restoring the Endangered Oyster Mussel (Epioblasma Capsaeformis) to the Upper Clinch River, Virginia: an Evaluation of Population Restoration Techniques Caitlin S
RESEARCH ARTICLE Restoring the endangered oyster mussel (Epioblasma capsaeformis) to the upper Clinch River, Virginia: an evaluation of population restoration techniques Caitlin S. Carey1,2,3,JessW.Jones4, Robert S. Butler5, Eric M. Hallerman6 From 2005 to 2011, the federally endangered freshwater mussel Epioblasma capsaeformis (oyster mussel) was reintroduced at three sites in the upper Clinch River, Virginia, using four release techniques. These release techniques were (1) translocation of adults (site 1, n = 1418), (2) release of laboratory-propagated sub-adults (site 1, n = 2851), (3) release of 8-week-old laboratory-propagated juveniles (site 2, n = 9501), and (4) release of artificially infested host fishes (site 3, n = 1116 host fishes). These restoration efforts provided a unique research opportunity to compare the effectiveness of techniques used to reestablish populations of extirpated and declining species. We evaluated the relative success of these four population restoration approaches via monitoring at each release site (2011–2012) using systematic 0.25-m2 quadrat sampling to estimate abundance and post-release survival. Abundances of translocated adult and laboratory-propagated sub-adult E. capsaeformis at site 1 ranged 577–645 and 1678–1700 individuals, respectively, signifying successful settlement and high post-release survival. Two untagged individuals (29.1 and 27.3 mm) were observed, indicating that recruitment is occurring at site 1. No E. capsaeformis were found at sites where 8-week-old laboratory-propagated juveniles (site 2) and artificially infested host fishes (site 3) were released. Our results indicate that translocations of adults and releases of laboratory-propagated sub-adults were the most effective population restoration techniques for E. -
Guiding Species Recovery Through Assessment of Spatial And
Guiding Species Recovery through Assessment of Spatial and Temporal Population Genetic Structure of Two Critically Endangered Freshwater Mussel Species (Bivalvia: Unionidae) Jess Walter Jones ( [email protected] ) United States Fish and Wildlife Service Timothy W. Lane Virginia Department of Game and Inland Fisheries N J Eric M. Hallerman Virginia Tech: Virginia Polytechnic Institute and State University Research Article Keywords: Freshwater mussels, Epioblasma brevidens, E. capsaeformis, endangered species, spatial and temporal genetic variation, effective population size, species recovery planning, conservation genetics Posted Date: March 16th, 2021 DOI: https://doi.org/10.21203/rs.3.rs-282423/v1 License: This work is licensed under a Creative Commons Attribution 4.0 International License. Read Full License Page 1/28 Abstract The Cumberlandian Combshell (Epioblasma brevidens) and Oyster Mussel (E. capsaeformis) are critically endangered freshwater mussel species native to the Tennessee and Cumberland River drainages, major tributaries of the Ohio River in the eastern United States. The Clinch River in northeastern Tennessee (TN) and southwestern Virginia (VA) harbors the only remaining stronghold population for either species, containing tens of thousands of individuals per species; however, a few smaller populations are still extant in other rivers. We collected and analyzed genetic data to assist with population restoration and recovery planning for both species. We used an 888 base-pair sequence of the mitochondrial NADH dehydrogenase 1 (ND1) gene and ten nuclear DNA microsatellite loci to assess patterns of genetic differentiation and diversity in populations at small and large spatial scales, and at a 9-year (2004 to 2013) temporal scale, which showed how quickly these populations can diverge from each other in a short time period. -
Meeting 22 Minutes
Thames – Sydenham and Region Source Protection Committee Meeting Notice Please be advised that a meeting of the Thames-Sydenham and Region Source Protection Committee has been called for the following time. If you are unable to attend please contact Erin Carroll at 519-245-3710x 46. Meeting Date: January 8, 2010 Meeting Time: 9:00 am to 3:00 pm Meeting Location: St. Clair Conservation Authority office Proposed Agenda Item Time 1. Chair’s Welcome 9:00 2. Adoption of the Agenda 3. Delegations 4. Minutes From the Previous Meeting 5. Declaration of Conflict of Interest 6. Business arising from the minutes a. Wallaceburg IPZ-2 (presentation) b. Tier 1 Water Budget 7. Business 10:00 a. LTV AR Sections i. Background ii. Watershed Characterization iii. Water Budget iv. Vulnerability Assessment v. Issues Evaluation vi. Conditions vii. Threats and Risk Assessment viii. Great Lakes ix. Data Gaps b. LTV AR Maps Lunch 12:00 c. LTV AR Threats Tables d. LTV AR System Summaries e. LTV AR Section Summaries f. For Approval - Notification of Significant Threats g. Meeting Schedule 8. Information a. Managed Lands Technical Bulletin b. Geothermal Technical Bulletin c. DRAFT - Deadstock Disposal Technical Bulletin 9. In Camera Session 10. Other business Page 1 of 13 11. MOE Liaison report 12. Members reports 13. Adjournment 3:00 Meeting Materials Agenda Item Description 2010.01.4. December minutes 2010.01.7a. LTV AR Sections 2010.017b. LTV Maps 2010.01.7c. LTV Threat tables 2010.01.7d. LTV System Summaries 2010.01.7e. LTV Section Summaries 2010.01.7fg Revised Meeting Schedule - To be distributed later 2010.01.8a. -
Freshwater Mussel Survey of Clinchport, Clinch River, Virginia: Augmentation Monitoring Site: 2006
Freshwater Mussel Survey of Clinchport, Clinch River, Virginia: Augmentation Monitoring Site: 2006 By: Nathan L. Eckert, Joe J. Ferraro, Michael J. Pinder, and Brian T. Watson Virginia Department of Game and Inland Fisheries Wildlife Diversity Division October 28th, 2008 Table of Contents Introduction....................................................................................................................... 4 Objective ............................................................................................................................ 5 Study Area ......................................................................................................................... 6 Methods.............................................................................................................................. 6 Results .............................................................................................................................. 10 Semi-quantitative .................................................................................................. 10 Quantitative........................................................................................................... 11 Qualitative............................................................................................................. 12 Incidental............................................................................................................... 12 Discussion........................................................................................................................ -
Mitchell's Bay, Dresden, Wallaceburg
CAIRO RD MAIN LINE 22 LAMBTON LINE 22 RD 40 26 ERICK COUNTY LIM MICHIGAN SARNIA COUNTY OF LAMBTON 121 ALGONAC ST. OF CLAIR 121 23 PETER RD. 31 BOTHWELL MIDDLESEX LANGSTAFF LINE 44 21 ARNOLD ROAD 25 ZONE CENTRE LINE 24 Legend FORHAN STREET 22 FERRY TO 33 PARKWAY 16 U.S. CROTON LINE 2 CLACHAN ROAD KIMBALL ROAD DAWN MILLS RD 29 McCREARY LINE ROAD ZONE ROAD 7 78 MANDAUMIN RD. McCREARY LINE HIGHWAY 40 23 78 IRISH SCHOOL RD. Airport 28 29 CROTON LINE 25 DUFFERIN AVE. 33 H SYDENHAM RIVER ROAD LONGWOODS SYDENHAM RIVER THAMES RIVER COUNTY 32 121 N WALLACEBURG VIA RAIL Angling 15 18 UNCLE FLORENCE ROAD OF LITTLEJOHN BASE LINE TOM'S Parks CLACHA BASE LINE 28 ROAD Blueberries 15 DRESDEN 26 ELGIN MURRAY ST. MURRAY Arena BASE LINE 15 ST. ROAD OAKDALE ROAD JANE ROAD 21 BASE LINE INDUSTRIAL RD. NORTH KENT BRIDGE ROAD FIRST NATIONS 21 2 FIRST NATIONS 29 JANE ST 121 Bed & Breakfast RESERVE 42 29A 28 RESERVE WALPOLE ISLAND LONDON THAMESVILLE MORAVIAN OF SELTON LINE Birding 40 401 15 CENTRE SIDE ROAD THE THAMESORFORD ROAD 121 29 18 iMaze Boat Launch ST. ANNE OLDFIELD LINE 21 ISLAND 2 ROAD 20 ST. CLAIR ROAD 19 ROBIN LINE Bus Terminal SELTON LINE LONGWOODS 29 RIVER LINE Orford Road 19 MUIRKIRK LINE ELECTRIC LINE Exit 117 Camping 18 GOODBRAND LINE 18 19 UNION LINE PRINCE ALBERT ROAD BEAR LINE ROADDOVER 2 VICTORIA ROAD CK Police 42 CENTRE 15 Victoria Road HIGHGATE DUART 28 SCANE ROAD BAY LINE FYSH LINE Exit 401 BURY RD. -
A Holistic Approach to Taxonomic Evaluation of Two Closely Related Endangered Freshwater Mussel Species, the Oyster Mussel Epiob
A HOLISTIC APPROACH TO TAXONOMIC EVALUATION OF TWO CLOSELY RELATED ENDANGERED FRESHWATER MUSSEL SPECIES, THE OYSTER MUSSEL EPIOBLASMA CAPSAEFORMIS AND TAN RIFFLESHELL EPIOBLASMA FLORENTINA WALKERI (BIVALVIA: UNIONIDAE) JESS W. JONES1, RICHARD J. NEVES2,STEVENA.AHLSTEDT3 AND ERIC M. HALLERMAN4 1U.S. Fish and Wildlife Service, Department of Fisheries and Wildlife Sciences, Virginia Polytechnic Institute and State University, Blacksburg, VA 24061-0321, U.S.A.; 2U.S. Geological Survey, Virginia Cooperative Fish and Wildlife Research Unit, Department of Fisheries and Wildlife Sciences, Virginia Polytechnic Institute and State University, Blacksburg, VA 24061-0321, U.S.A.; 3U.S. Geological Survey, 1820 Midpark Drive, Knoxville, TN 37921, U.S.A.; 4Department of Fisheries and Wildlife Sciences, Virginia Polytechnic Institute and State University, Blacksburg, VA 24061-0321, U.S.A. (Received 23 February 2005; accepted 16 January 2006) ABSTRACT Species in the genus Epioblasma have specialized life history requirements and represent the most endangered genus of freshwater mussels (Unionidae) in the world. A genetic characterization of extant populations of the oyster mussel E. capsaeformis and tan riffleshell E. florentina walkeri sensu late was conducted to assess taxonomic validity and to resolve conservation issues for recovery planning. These mussel species exhibit pronounced phenotypic variation, but were difficult to characterize phylogenetically using DNA sequences. Monophyletic lineages, congruent with phenotypic variation among species, were obtained only after extensive analysis of combined mitochondrial (1396 bp of 16S, cytochrome-b, and ND1) and nuclear (515 bp of ITS-1) DNA sequences. In contrast, analysis of variation at 10 hypervariable DNA microsatellite loci showed moderately to highly diverged populations based on FST and RST values, which ranged from 0.12 to 0.39 and 0.15 to 0.71, respectively. -
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 a Heritage Impact Assessment Report
APPENDIX A HERITAGE IMPACT ASSESSMENT REPORT October 9, 2015 HERITAGE IMPACT ASSESSMENT Holt Line Bridge (Duthill Bridge/10th Concession Bridge) Spanning the Sydenham River, St. Clair Township, Ontario Submitted to: Kelly Vader, MCIP, RPP BM Ross and Associates Limited 62 North Street Goderich, ON N7A 2TA Report Number: 1534665-R01 Distribution: 1 Copy - BM Ross and Associates Limited REPORT 1 Copy - Golder Associates Ltd. HIA - HOLT LINE BRIDGE - TOWNSHIP OF ST. CLAIR Executive Summary Golder Associates Ltd. was retained by B.M. Ross and Associates Ltd. (B.M. Ross) to undertake a Heritage Impact Assessment (HIA) for the proposed rehabilitation or replacement of the of the Duthill Bridge, also known as the Holt Line Bridge, located on Holt Line in the Township of St. Clair, Ontario. The objective of the HIA was to determine whether the structure represented a built heritage resource or a part of a cultural heritage landscape of cultural heritage value or interest. The analysis of the Duthill Bridge was guided by the Ontario Ministry of Tourism, Culture, and Sport’s (MTCS) Ontario Heritage Toolkit: Heritage Resources in the Land Use Planning Process. This HIA makes the following recommendations: Subject to the confirmation of preferred alternatives for the potential rehabilitation or replacement of the Duthill Bridge, St. Clair Township should consider the mitigation options identified in Section 5.3 of this report to evaluate the potential options that would conserve the cultural heritage value of the bridge. From a best practice standpoint for the conservation of heritage resources, the preferred alternative for the Duthill Bridge would be one of the following three options: Construction of a new bridge adjacent to the existing structure: The retention of the bridge in situ as a part of a pedestrian or recreational vehicle crossing would act as a form of mitigation. -
Native Freshwater Mussels
Native Freshwater Mussels January 2007 Fish and Wildlife Habitat Management Leaflet Number 46 Introduction Freshwater mussels belong to the phylum Mollusca, the second most diverse group of animals in the world in terms of number of described species. The phy- lum consists of approximately 100,000 freshwater, marine, and terrestrial species and includes mussels, snails, octopi, squid, as well as several other less fa- miliar groups. Although freshwater mussels are dis- tributed throughout the world, they reach their great- est diversity in North America, east of the Mississippi River. United States mussel populations have been in Virginia Department of Game and Inland Fisheries decline since the late 1800s for a number of reasons. Although freshwater mussels are found throughout Currently, nearly three-quarters of North America’s much of the world, they reach their greatest diversity native freshwater mussel species are considered en- in North America. dangered, threatened, or species of special concern, and some researchers believe that as many as 35 spe- cies (12%) are already extinct. >80 species The objective of this leaflet is to raise awareness 71–80 species about the decline of freshwater mussels in North 61–70 species America, their life history requirements, and the im- 51–60 species 41–50 species portant ecological role they play in aquatic habitats. 31–40 species In addition, this leaflet provides a number of practi- 21–30 species cal habitat management considerations to help pro- 11–20 species tect freshwater mussel populations. Freshwater mus- 1–10 species sels can also be referred to as freshwater clams or Adapted from presentation of Kevis S. -
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 .......................................................................................