Differences in Brain Transcriptomes of Closely Related Baikal Coregonid Species
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Lake Baikal Russian Federation
LAKE BAIKAL RUSSIAN FEDERATION Lake Baikal is in south central Siberia close to the Mongolian border. It is the largest, oldest by 20 million years, and deepest, at 1,638m, of the world's lakes. It is 3.15 million hectares in size and contains a fifth of the world's unfrozen surface freshwater. Its age and isolation and unusually fertile depths have given it the world's richest and most unusual lacustrine fauna which, like the Galapagos islands’, is of outstanding value to evolutionary science. The exceptional variety of endemic animals and plants make the lake one of the most biologically diverse on earth. Threats to the site: Present threats are the untreated wastes from the river Selenga, potential oil and gas exploration in the Selenga delta, widespread lake-edge pollution and over-hunting of the Baikal seals. However, the threat of an oil pipeline along the lake’s north shore was averted in 2006 by Presidential decree and the pulp and cellulose mill on the southern shore which polluted 200 sq. km of the lake, caused some of the worst air pollution in Russia and genetic mutations in some of the lake’s endemic species, was closed in 2009 as no longer profitable to run. COUNTRY Russian Federation NAME Lake Baikal NATURAL WORLD HERITAGE SERIAL SITE 1996: Inscribed on the World Heritage List under Natural Criteria vii, viii, ix and x. STATEMENT OF OUTSTANDING UNIVERSAL VALUE The UNESCO World Heritage Committee issued the following statement at the time of inscription. Justification for Inscription The Committee inscribed Lake Baikal the most outstanding example of a freshwater ecosystem on the basis of: Criteria (vii), (viii), (ix) and (x). -
Burbot Management Plan
BURBOT MANAGEMENT PLAN DEPARTMENT OF INLAND FISHERIES AND WILDLIFE DIVISION OF FISHERIES AND HATCHERIES PREPARED BY SCOTT A. ROY ASSISTANT REGIONAL FISHERIES BIOLOGIST REGION E MARCH 2001 BURBOT LIFE HISTORY The burbot, Lota lota (Linnaeus), is a unique member of the cod family. It is the only species in the family, which spends its entire life in fresh water. However, the burbot is similar to its marine relatives in that its distribution is circumpolar. It can be found in cool, fresh waters throughout northern Europe, Asia and North America. In North America its range extends as far south as the northern tier of States across the United States. In Maine, the burbot is commonly known as the cusk, although in other areas it is also called the ling, eelpout, loche and lawyer. Unlike the salmonids and Maine’s other coldwater species, the burbot is not noted for its grace and beauty. The body is elongate, almost eel-shaped, with long, soft-rayed dorsal and anal fins that meet a rounded tail. Although it is smooth and slimy to the touch, the skin is embedded with very small, cycloid scales. The head of the burbot is broad and somewhat flattened. It has a large mouth containing several rows of small teeth on the jaws. A single, whisker-like barbell protrudes from the tip of the chin. There are no obvious external differences between males and females. In general, adults are olive brown to dark brown on the back and sides. This background is overlaid with distinctive patterns of dark brown or black markings and spots. -
Sport-Fish-Identification.Pdf
Walleye Walleye have two distinct fins on their back, the first with large spines. Lake Sturgeon They have a yellow-olive back, brassy, silvery sides with yellow spots, a white underside, and white on the lower lobe of the tail. Dusky vertical Lake Sturgeon are a Threatened Species due to population size and bars are often found on the body as well. concerns with viability. Lake Sturgeon have a large brown or grey body covered with tough, leather- like tissue and five rows of bony plates. They have a shark-like, upturned tail and a pointed snout with four barbels. Sauger Lake Whitefish are olive-green to blue on the back, with silvery sides.They Sauger are a Threatened Species due to hybridization, habitat Lakehave a small Whitefish mouth below a rounded snout, and a deeply forked tail. degradation and overharvest. Sauger are golden olive on the back with silver-yellow sides and a white underside. They also have a large spiny dorsal fin, distinct rows of spots on the dorsal fins and three or four dusky vertical bars on the body. Mountain Whitefish have large scales, no spots and small mouths with no Burbot Mountainteeth. Their general Whitefish body colour is a bronze-white or greenish white. Burbot have a slim, brownish black body with smooth skin, a flattened head, and a fin that stretches along the back half of the body. Distinctive barbels hang from the lower jaw and nostrils. Goldeye Northern Pike Goldeye have prominent eyes with bright yellow pupils, a blunt head, and Northern Pike are a long, slender fish with duck-like jaws and a long, flat a deep, compressed body. -
Westslope Cutthroat Trout
This file was created by scanning the printed publication. Errors identified by the software have been corrected; Chapter 1 however, some errors may remain. Westslope Cutthroat Trout John D. IVIclntyre and Bruce E. Rieman, USDA Forest Service, Intermountain Research Station, 316 E. iViyrtle Street, Boise, Idaho 83702 Introduction Westslope cutthroat trout begin to mature at age 3 but usually spawn first at age 4 or 5 (table 2). Sexu The westslope cutthroat trout inhabits streams on ally maturing adfluvial fish move into the vicinity of both sides of the Continental Divide. On the east side tributaries in fall and winter where they remain un of the divide, they are distributed mostly in Mon til they begin to migrate upstream in the spring tana but also occur in some headwaters in Wyoming (Liknes 1984). They spawn from March to July at and southern Alberta (Behnke 1992). They are in the water temperatures near 10°C (Roscoe 1974; Liknes Missouri Basin downstream to about 60 km below 1984; Shepard et al. 1984). A population of adult fish Great Falls and in the headwaters of the Judith, Milk, in the St. Joe River, Idaho, included 1.6 females for and Marias rivers. On the west side of the Continen each male (Thurow and Bjornn 1978). Average length tal Divide the subspecies occurs in the upper was 334 mm for females and 366 mm for males. A Kootenai River; the Clark Fork drainage in Montana similar population in Big Creek, Montana, included and Idaho downstream to the falls on the Fend Oreille 4.1 females for each male (Huston et al. -
Decision of the Government of the Russian Federation No. 908 of December 31, 2004 on the Approval of the Lists of the Codes of T
DECISION OF THE GOVERNMENT OF THE RUSSIAN FEDERATION NO. 908 OF DECEMBER 31, 2004 ON THE APPROVAL OF THE LISTS OF THE CODES OF THE TYPES OF FOODSTUFFS AND GOODS FOR CHILDREN IMPOSABLE WITH VALUE-ADDED TAX AT THE 10 PER CENT TAX RATE (with the Amendments and Addenda of March 23, October 12, 2005, February 27, November 27, December 30, 2006, July 9, 23, 2007) In accordance with Subitems 1 and 2 of Item 2 of Article 164 of the Tax Code of the Russian Federation, the Government of the Russian Federation resolves as follows: 1. To approve the annexed: List of the Codes of the Types of Foodstuffs in Accordance with the All-Russia Classifier of Products Imposable with Value-Added Tax at the 10 per Cent Tax Rate in Their Realisation; List of the Codes of the Types of Foodstuffs in Accordance with the Commodity Classification of Foreign Economic Activity of the Russian Federation Imposable with Value-Added Tax at the 10 per Cent Tax Rate in Their Importation into the Customs Territory of the Russian Federation; List of the Codes of the Types of Goods for Children in Accordance with the All-Russia Classifier of Products Imposable with Value-Added Tax at the 10 per Cent Tax Rate in Their Realisation; List of the Codes of the Types of Goods for Children in Accordance with the Commodity Classification of Foreign Economic Activity of the Russian Federation Imposable with Value-Added Tax at the 10 per Cent Tax in Their Importation into the Customs Territory of the Russian Federation. -
Lake Superior Food Web MENT of C
ATMOSPH ND ER A I C C I A N D A M E I C N O I S L T A R N A T O I I O T N A N U E .S C .D R E E PA M RT OM Lake Superior Food Web MENT OF C Sea Lamprey Walleye Burbot Lake Trout Chinook Salmon Brook Trout Rainbow Trout Lake Whitefish Bloater Yellow Perch Lake herring Rainbow Smelt Deepwater Sculpin Kiyi Ruffe Lake Sturgeon Mayfly nymphs Opossum Shrimp Raptorial waterflea Mollusks Amphipods Invasive waterflea Chironomids Zebra/Quagga mussels Native waterflea Calanoids Cyclopoids Diatoms Green algae Blue-green algae Flagellates Rotifers Foodweb based on “Impact of exotic invertebrate invaders on food web structure and function in the Great Lakes: NOAA, Great Lakes Environmental Research Laboratory, 4840 S. State Road, Ann Arbor, MI A network analysis approach” by Mason, Krause, and Ulanowicz, 2002 - Modifications for Lake Superior, 2009. 734-741-2235 - www.glerl.noaa.gov Lake Superior Food Web Sea Lamprey Macroinvertebrates Sea lamprey (Petromyzon marinus). An aggressive, non-native parasite that Chironomids/Oligochaetes. Larval insects and worms that live on the lake fastens onto its prey and rasps out a hole with its rough tongue. bottom. Feed on detritus. Species present are a good indicator of water quality. Piscivores (Fish Eaters) Amphipods (Diporeia). The most common species of amphipod found in fish diets that began declining in the late 1990’s. Chinook salmon (Oncorhynchus tshawytscha). Pacific salmon species stocked as a trophy fish and to control alewife. Opossum shrimp (Mysis relicta). An omnivore that feeds on algae and small cladocerans. -
Bear Lake Whitefish Prosopium Abyssicola
Bear Lake Whitefish Prosopium abyssicola Actinopterygii — Salmoniformes — Salmonidae CONSERVATION STATUS / CLASSIFICATION Rangewide: Critically imperiled (G1) Statewide: Critically imperiled (S1) ESA: No status USFS: Region 1: No status; Region 4: No status BLM: Rangewide/Globally imperiled (Type 2) IDFG: Game fish BASIS FOR INCLUSION Endemic to Bear Lake. TAXONOMY The Bear Lake whitefish is 1 of 3 sympatric members of the genus Prosopium. No subspecies has been proposed. DISTRIBUTION AND ABUNDANCE This species is endemic to Bear Lake. POPULATION TREND Monitoring for >20 years indicates the population is stable (Nielson and Tolentino 2002). HABITAT AND ECOLOGY The Bear Lake whitefish typically occurs in the benthic zone at water depths greater than 40 m (130 ft). Spawning occurs in mid–February to mid–March in shallow, rocky areas. Ostracods comprise the majority of the diet, but other invertebrates found on the lake bottom may be consumed. ISSUES The lowering of lake levels due to natural events and anthropogenic actions could limit spawning and rearing habitat. Increasing human development around the lake could lead to lowering of water quality due to waste water discharges. Legal and illegal introductions of piscivorous fish could affect populations by increased predation rate. RECOMMENDED ACTIONS Continue programs that (1) monitor the population status and trend; (2) evaluate the relationship between water quality and level and fish populations; (3) stock sterile triploid lake trout; and (4) removal of illegally introduced non–native fish (e.g., walleye) in conjuction with adjacent states. Bear Lake Whitefish Prosopium abyssicola Ecological Section Species Range 10 August 2005 Fish information is from Idaho Fish and Wildlife 0 20 40 80 Kilometers Information System, Idaho Deptartment of Fish and Game and displayed at the 6th code hydrologic unit. -
Status of Burbot Populations in the Laurentian Great Lakes
American Fisheries Society Symposium 59:111–130, 2008 © 2008 by the American Fisheries Society Status of Burbot Populations in the Laurentian Great Lakes MARTIN A. STAPANIAN* U.S. Geological Survey, Great Lakes Science Center, Lake Erie Biological Station 6100 Columbus Avenue, Sandusky, Ohio 44870, USA CHARLES P. MADENJIAN U.S. Geological Survey, Great Lakes Science Center 1451 Green Road, Ann Arbor, Michigan 48105, USA CHARLES R. BRONTE U.S. Fish and Wildlife Service, Green Bay Fishery Resources Office 2661 Scott Tower Drive, New Franken, Wisconsin 54229, USA MARK P. EBENER Inter-Tribal Fisheries and Assessment Program, Chippewa Ottawa Resource Authority 179 West Three Mile Road, Sault Sainte Marie, Michigan 49783, USA BRIAN F. LANTRY U.S. Geological Survey, Great Lakes Science Center, Lake Ontario Biological Station 17 Lake Street, Oswego, New York 13126, USA JASON D. STOCKWELL U.S. Geological Survey, Great Lakes Science Center, Lake Superior Biological Station, 2800 Lakeshore Drive, Ashland, Wisconsin 54806, USA ABSTRACT.—Burbot Lota lota populations collapsed in four of the five Laurentian Great Lakes between 1930 and the early 1960s. Collapses in Lakes Michigan, Hu- ron, and Ontario were associated with sea lamprey Petromyzon marinus predation, whereas the collapse in Lake Erie was likely due to a combination of overexploita- tion, decreased water quality, and habitat degradation. We examined time series for burbot population density in all five lakes extending as far back as the early 1970s to present time and characterized the long-term trends after the initial collapses. Burbot population density in Lake Superior has remained relatively low and stable since 1978. -
Variation in the Abundance of Arctic Cisco in the Colville River: Analysis of Existing Data and Local Knowledge
OCS Study MMS 2007-042 VARIATION IN THE ABUNDANCE OF ARCTIC CISCO IN THE COLVILLE RIVER: ANALYSIS OF EXISTING DATA AND LOCAL KNOWLEDGE VOLUME II: FINAL REPORT APPENDICES November 2007 Prepared for The U.S. Department of the Interior Minerals Management Service Alaska Outer Continental Shelf Region Environmental Studies Section 3801 Centerpoint Drive, Suite 500 Anchorage, AK 99503-5823 Contract No.: 1435-01-04-CT-34979 Prepared by ABR, Inc.–Environmental Research & Services Sigma Plus, Statistical Consulting Services Stephen R. Braund & Associates Kuukpik Subsistence Oversight Panel, Inc. OCS Study MMS 2007-042 VARIATION IN THE ABUNDANCE OF ARCTIC CISCO IN THE COLVILLE RIVER: ANALYSIS OF EXISTING DATA AND LOCAL KNOWLEDGE VOLUME II: FINAL REPORT APPENDICES November 2007 Principal Investigator: Stephen M. Murphy ABR, Inc.–Environmental Research & Services Co-principal Investigator: Franz J. Mueter Sigma Plus, Statistical Consulting Services Co-principal Investigator: Stephen R. Braund Stephen R. Braund & Associates ABR, Inc.—Environmental Research & Services P.O. Box 80410 Fairbanks, AK 99708-0410 This study was funded by the U.S. Department of the Interior, Minerals Management Service (MMS), Alaska Outer Continental Shelf Region, Anchorage, Alaska, under Contract No. 1435- 01-04-CT-34979, as part of the MMS Environmental Studies Program. Disclaimer: The opinions, findings, conclusions, or recommendations expressed in this report or product are those of the authors and do not necessarily reflect the views of the U.S. Department of the Interior, nor does mention of trade names or commercial products constitute endorsement or recommendation for use by the federal government. OCS Study MMS 2007-042 TABLE OF CONTENTS Appendix A. -
Developing Research Priorities for Lake Whitefish in the Upper Great
DEVELOPING RESEARCH PRIORITIES FOR LAKE WHITEFISH IN THE UPPER GREAT LAKES: RESULTS OF A WORKSHOP SPONSORED BY THE GREAT LAKES FISHERY TRUST AND GREAT LAKES FISHERY COMMISSION Michigan State University February 27-28, 2018 Michigan Sea Grant Executive Summary ......................................................................................................................... 3 Workshop Proceedings ................................................................................................................... 3 Introduction ................................................................................................................................ 3 Workshop Goals and Desired Outcomes ............................................................................. 4 Presentations ....................................................................................................................... 4 Impacts of Whitefish Decline on the Tribal Commercial Fishery ..................................... 4 Lake Huron Lake Whitefish Status and Trends ................................................................ 5 Lake Michigan Lake Whitefish Status and Trends ............................................................ 7 Lake Superior Lake Whitefish Status and Trends ............................................................. 8 Lower Trophic Levels ........................................................................................................ 9 Factors affecting recruitment to fisheries and management implications .................. -
Long Lake FIN Summary 2017
Long Lake FIN Summary, 2017 Background “How are the fish in my lake doing?” We need this answer determine the most appropriate sport fishing regulations for to set appropriate fishing regulations, to understand and a lake. This landscape-level assessment allows for consistent, correct any problems with fish habitat, and to guard against broad temporal comparisons of fish sustainability and status. invasive species. A healthy fish population and fish For more information please see Alberta’s FIN and FSI community means we can all enjoy the benefits of websites, sustainable fisheries and healthy ecosystems. A standard method of assessing the status of fish populations is http://aep.alberta.ca/fish-wildlife/fisheries- necessary to allow comparisons of fish sustainability across management/fall-index-netting/default.aspx the years at a lake, and to compare to other lakes. In http://aep.alberta.ca/fish-wildlife/fisheries- Alberta, we use an accepted standard of index netting for management/fish-sustainability-index/default.aspx lake fisheries assessment. This method provides the necessary data on fish abundance, biological data (such as Table 1 – Alberta’s Fish Sustainability Index risk thresholds for age and sex), and species diversity to assess sustainability. Walleye and Northern Pike using the standardized Fall Index Net (FIN) method. Note: Thresholds align with species Fall Index Netting (FIN) management frameworks. Alberta Environment and Parks monitor Walleye and Mature Mature Risk to Northern Pike populations using standardized index netting Walleyes/net Pike/net Sustainability (Morgan, 2002). Fall index netting occurs during late summer >29.0 >21.8 Very Low and fall when water temperatures are 10-15 °C. -
Strategy for the Establishment of Self-Sustaining Atlantic Whitefish Population(S) and Development of a Framework for the Evaluation of Suitable Lake Habitat
Canadian Science Advisory Secretariat Maritimes Region Science Advisory Report 2018/045 STRATEGIES FOR THE ESTABLISHMENT OF SELF- SUSTAINING ATLANTIC WHITEFISH POPULATION(S) AND DEVELOPMENT OF A FRAMEWORK FOR THE EVALUATION OF SUITABLE LAKE HABITAT Atlantic Whitefish (Coregonus huntsmani) (Source: DFO 2009) Figure 1. Global distribution of Atlantic Whitefish. Context: The Atlantic Whitefish (Coregonus huntsmani) is an endangered species that is at high risk for global extinction. The species global distribution has been restricted, for at least the past three decades, to three small interconnected lakes in the upper Petite Rivière watershed in southwest Nova Scotia. The continued survival of Atlantic Whitefish is now further threatened by illegally introduced invasive piscivorous fish species (Smallmouth Bass (pre-2003) and Chain Pickerel (2013)) within this remaining habitat. Range expansion, the establishment of additional self-sustaining populations outside the currently occupied habitat in the Petite Rivière watershed, is identified as the distribution objective of the Atlantic Whitefish Recovery Strategy and could also prevent extinction. In spring 2017, three options in support of survival and recovery of Atlantic Whitefish were considered by Fisheries and Oceans Canada (DFO). Options included: simple translocation, translocation with temporary holding, and the establishment of a new propagation program at a DFO Biodiversity Facility with the option of translocation with temporary holding approved. This option would see Atlantic Whitefish, captured from the Petite Rivière Lakes, transported to a DFO Biodiversity Facility for short-term holding, before being released into new non- natal habitat. However, insufficient numbers of Atlantic Whitefish are available from the wild to provide a reasonable likelihood of success of this option at present.