Identification of Larvae of Three Arctic Species of Limanda (Family Pleuronectidae)
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Pleuronectidae, Poecilopsettidae, Achiridae, Cynoglossidae
1536 Glyptocephalus cynoglossus (Linnaeus, 1758) Pleuronectidae Witch flounder Range: Both sides of North Atlantic Ocean; in the western North Atlantic from Strait of Belle Isle to Cape Hatteras Habitat: Moderately deep water (mostly 45–330 m), deepest in southern part of range; found on mud, muddy sand or clay substrates Spawning: May–Oct in Gulf of Maine; Apr–Oct on Georges Bank; Feb–Jul Meristic Characters in Middle Atlantic Bight Myomeres: 58–60 Vertebrae: 11–12+45–47=56–59 Eggs: – Pelagic, spherical Early eggs similar in size Dorsal fin rays: 97–117 – Diameter: 1.2–1.6 mm to those of Gadus morhua Anal fin rays: 86–102 – Chorion: smooth and Melanogrammus aeglefinus Pectoral fin rays: 9–13 – Yolk: homogeneous Pelvic fin rays: 6/6 – Oil globules: none Caudal fin rays: 20–24 (total) – Perivitelline space: narrow Larvae: – Hatching occurs at 4–6 mm; eyes unpigmented – Body long, thin and transparent; preanus length (<33% TL) shorter than in Hippoglossoides or Hippoglossus – Head length increases from 13% SL at 6 mm to 22% SL at 42 mm – Body depth increases from 9% SL at 6 mm to 30% SL at 42 mm – Preopercle spines: 3–4 occur on posterior edge, 5–6 on lateral ridge at about 16 mm, increase to 17–19 spines – Flexion occurs at 14–20 mm; transformation occurs at 22–35 mm (sometimes delayed to larger sizes) – Sequence of fin ray formation: C, D, A – P2 – P1 – Pigment intensifies with development: 6 bands on body and fins, 3 major, 3 minor (see table below) Glyptocephalus cynoglossus Hippoglossoides platessoides Total myomeres 58–60 44–47 Preanus length <33%TL >35%TL Postanal pigment bars 3 major, 3 minor 3 with light scattering between Finfold pigment Bars extend onto finfold None Flexion size 14–20 mm 9–19 mm Ventral pigment Scattering anterior to anus Line from anus to isthmus Early Juvenile: Occurs in nursery habitats on continental slope E. -
Bristol Bay, Alaska
EPA 910-R-14-001C | January 2014 An Assessment of Potential Mining Impacts on Salmon Ecosystems of Bristol Bay, Alaska Volume 3 – Appendices E-J Region 10, Seattle, WA www.epa.gov/bristolbay EPA 910-R-14-001C January 2014 AN ASSESSMENT OF POTENTIAL MINING IMPACTS ON SALMON ECOSYSTEMS OF BRISTOL BAY, ALASKA VOLUME 3—APPENDICES E-J U.S. Environmental Protection Agency Region 10 Seattle, WA CONTENTS VOLUME 1 An Assessment of Potential Mining Impacts on Salmon Ecosystems of Bristol Bay, Alaska VOLUME 2 APPENDIX A: Fishery Resources of the Bristol Bay Region APPENDIX B: Non-Salmon Freshwater Fishes of the Nushagak and Kvichak River Drainages APPENDIX C: Wildlife Resources of the Nushagak and Kvichak River Watersheds, Alaska APPENDIX D: Traditional Ecological Knowledge and Characterization of the Indigenous Cultures of the Nushagak and Kvichak Watersheds, Alaska VOLUME 3 APPENDIX E: Bristol Bay Wild Salmon Ecosystem: Baseline Levels of Economic Activity and Values APPENDIX F: Biological Characterization: Bristol Bay Marine Estuarine Processes, Fish, and Marine Mammal Assemblages APPENDIX G: Foreseeable Environmental Impact of Potential Road and Pipeline Development on Water Quality and Freshwater Fishery Resources of Bristol Bay, Alaska APPENDIX H: Geologic and Environmental Characteristics of Porphyry Copper Deposits with Emphasis on Potential Future Development in the Bristol Bay Watershed, Alaska APPENDIX I: Conventional Water Quality Mitigation Practices for Mine Design, Construction, Operation, and Closure APPENDIX J: Compensatory Mitigation and Large-Scale Hardrock Mining in the Bristol Bay Watershed AN ASSESSMENT OF POTENTIAL MINING IMPACTS ON SALMON ECOSYSTEMS OF BRISTOL BAY, ALASKA VOLUME 3—APPENDICES E-J Appendix E: Bristol Bay Wild Salmon Ecosystem: Baseline Levels of Economic Activity and Values Bristol Bay Wild Salmon Ecosystem Baseline Levels of Economic Activity and Values John Duffield Chris Neher David Patterson Bioeconomics, Inc. -
Aspects of the Life History of Hornyhead Turbot, Pleuronichthys Verticalis, Off Southern California
Aspects of the Life History of Hornyhead Turbot, Pleuronichthys verticalis, off Southern California he hornyhead turbot T(Pleuronichthys verticalis) is a common resident flatfish on the mainland shelf from Magdalena Bay, Baja Califor- nia, Mexico to Point Reyes, California (Miller and Lea 1972). They are randomly distributed over the bottom at a density of about one fish per 130 m2 and lie partially buried in the sediment (Luckinbill 1969). Hornyhead turbot feed primarily on sedentary, tube-dwelling polychaetes (Luckinbill 1969, Allen 1982, Cross et al. 1985). They pull the tubes from the sediment, Histological section of a fish ovary. extract the polychaete, and then eject the tube (Luckinbill 1969). Hornyhead turbot are Orange County, p,p’-DDE Despite the importance of batch spawners and may averaged 362 μg/kg wet the hornyhead turbot in local spawn year round (Goldberg weight in hornyhead turbot monitoring programs, its life 1982). Their planktonic eggs liver and 5 μg/kg dry weight in history has received little are 1.00-1.16 mm diameter the sediments (CSDOC 1992). attention. The long-term goal (Sumida et al. 1979). Their In the same year in Santa of our work is to determine larvae occur in the nearshore Monica Bay, p,p’-DDE aver- how a relatively low trophic plankton throughout the year aged 7.8 mg/kg wet weight in level fish like the hornyhead (Gruber et al. 1982, Barnett et liver and 81 μg/kg dry weight turbot accumulates tissue al. 1984, Moser et al. 1993). in the sediments (City of Los levels of chlorinated hydrocar- Several agencies in South- Angeles 1992). -
Supplementary Tales
Metabarcoding reveals different zooplankton communities in northern and southern areas of the North Sea Jan Niklas Macher, Berry B. van der Hoorn, Katja T. C. A. Peijnenburg, Lodewijk van Walraven, Willem Renema Supplementary tables 1-5 Table S1: Sampling stations and recorded abiotic variables recorded during the NICO 10 expedition from the Dutch Coast to the Shetland Islands Sampling site name Coordinates (°N, °E) Mean remperature (°C) Mean salinity (PSU) Depth (m) S74 59.416510, 0.499900 8.2 35.1 134 S37 58.1855556, 0.5016667 8.7 35.1 89 S93 57.36046, 0.57784 7.8 34.8 84 S22 56.5866667, 0.6905556 8.3 34.9 220 S109 56.06489, 1.59652 8.7 35 79 S130 55.62157, 2.38651 7.8 34.8 73 S156 54.88581, 3.69192 8.3 34.6 41 S176 54.41489, 4.04154 9.6 34.6 43 S203 53.76851, 4.76715 11.8 34.5 34 Table S2: Species list and read number per sampling site Class Order Family Genus Species S22 S37 S74 S93 S109 S130 S156 S176 S203 Copepoda Calanoida Acartiidae Acartia Acartia clausi 0 0 0 72 0 170 15 630 3995 Copepoda Calanoida Acartiidae Acartia Acartia tonsa 0 0 0 0 0 0 0 0 23 Hydrozoa Trachymedusae Rhopalonematidae Aglantha Aglantha digitale 0 0 0 0 1870 117 420 629 0 Actinopterygii Trachiniformes Ammodytidae Ammodytes Ammodytes marinus 0 0 0 0 0 263 0 35 0 Copepoda Harpacticoida Miraciidae Amphiascopsis Amphiascopsis cinctus 344 0 0 992 2477 2500 9574 8947 0 Ophiuroidea Amphilepidida Amphiuridae Amphiura Amphiura filiformis 0 0 0 0 219 0 0 1470 63233 Copepoda Calanoida Pontellidae Anomalocera Anomalocera patersoni 0 0 586 0 0 0 0 0 0 Bivalvia Venerida -
Current Situation, Trends and Prospects in World Capture Fisheries‘
JUNE 1995 CURRENT SITUATION, TRENDS AND PROSPECTS IN WORLD CAPTURE FISHERIES‘ S.M. Garcia and C. Newton FAO Fisheries- Department, Rome, Italy Abstract Following an earlier analysis provided by FAO (19931, the paper gives an update of the trends and future perspectives of world fisheries. It describes and comments on worldwide trends in landings, trade, prices and fleet size. It illustrates the decrease in landings in the last 3 years, the relationship between landings and prices and the large overcapacity in world fishing fleets. It provides a review of the state of world fishery resources, globally, by region and species groups, as well as a brief account of environmental impacts on fisheries. It presents an economic perspective for world fisheries which underlines further the overcapacity and subsidy issues that characterize modern fisheries. In conclusion, it discusses‘management issues including the need for fleet reduction policies, the potential combined effect of international trade on resources depletion in developing exporting countries, throwing into question the overall sustainability of the world fishery system. LIST OF FIGURES Fig. 1: Evolution of fishery production since 1800 (modified from Hilborn, 1992). Fig. 2: Total reported catches from marine fisheries(?950-1 992). Fig. 3: World catch of demersal species (1970-1 992) Fig. 4: World catch of pelagic species (1970-1 992) P’ Fig. 5: Production of flatfish, tuna and shrimp (including culture) (1970-92) 3 Fig. 6: Value of major species and group of species and cumulative ‘Paper presented at the Conference on Fisheries Management. Global trends. Seattle (Washington, USA), 14-16 June 1994 2 percentage of world total in 1970 (A) and 1992 (BI. -
Assessment of the Other Flatfish Stock Complex in the Bering Sea and Aleutian Islands
11. Assessment of the other flatfish stock complex in the Bering Sea and Aleutian Islands Thomas K. Wilderbuer and Daniel G. Nichol Executive Summary Summary of Changes in Assessment Inputs Changes in the Input Data 1) The 2013 catch (total and discarded) was updated, and catch through 26 October, 2013 were included in the assessment. 2) The 2013 Eastern Bering Sea shelf survey biomass estimates and standard errors of other flatfish species are included in the assessment. Changes in the Assessment Methodology 1) There were no changes in the assessment methodology. Summary of Results A summary of the 2013 recommended ABCs and OFLs (in bold) relative to the 2012 recommendations for Other flatfish in the Bering Sea/Aleutian Islands (BSAI) is as follows: As estimated or As estimated or specified last year for: recommended this year for: Quantity 2013 2014 2014 2015 M (natural mortality rate) for rex sole 0.17 0.17 0.17 0.17 M (natural mortality rate) for Dover sole 0.085 0.085 0.085 0.085 M (natural mortality rate) for all others 0.15 0.15 0.15 0.15 Tier 5 5 5 5 Biomass (t) 114,200 114,200 107,500 107,500 FOFL (F=M) for rex sole 0.17 0.17 0.17 0.17 FOFL (F=M) for Dover sole 0.085 0.085 0.085 0.085 FOFL (F=M) for all other species 0.15 0.15 0.15 0.15 maxFABC for rex sole 0.13 0.13 0.13 0.13 maxFABC for Dover sole 0.064 0.064 0.064 0.064 maxFABC for all other species 0.113 0.113 0.113 0.113 FABC for rex sole 0.13 0.13 0.13 0.13 FABC for Dover sole 0.064 0.064 0.064 0.064 FABC for all other species 0.113 0.113 0.113 0.113 OFL (t) 17,800 17,800 16,700 16,700 maxABC (t) 13,300 13,300 12,400 12,400 ABC (t) 13,300 13,300 12,400 12,400 As determined last year for: As determined this year for: Status 2011 2012 2012 2013 Overfishing n/a n/a n/a n/a Responses to SSC and Plan Team Comments to Assessments in General There were no comments relative to the other flatfish assessment. -
Fishery Management Plan for Groundfish of the Bering Sea and Aleutian Islands Management Area APPENDICES
FMP for Groundfish of the BSAI Management Area Fishery Management Plan for Groundfish of the Bering Sea and Aleutian Islands Management Area APPENDICES Appendix A History of the Fishery Management Plan ...................................................................... A-1 A.1 Amendments to the FMP ......................................................................................................... A-1 Appendix B Geographical Coordinates of Areas Described in the Fishery Management Plan ..... B-1 B.1 Management Area, Subareas, and Districts ............................................................................. B-1 B.2 Closed Areas ............................................................................................................................ B-2 B.3 PSC Limitation Zones ........................................................................................................... B-18 Appendix C Summary of the American Fisheries Act and Subtitle II ............................................. C-1 C.1 Summary of the American Fisheries Act (AFA) Management Measures ............................... C-1 C.2 Summary of Amendments to AFA in the Coast Guard Authorization Act of 2010 ................ C-2 C.3 American Fisheries Act: Subtitle II Bering Sea Pollock Fishery ............................................ C-4 Appendix D Life History Features and Habitat Requirements of Fishery Management Plan SpeciesD-1 D.1 Walleye pollock (Theragra calcogramma) ............................................................................ -
Collapse and Recovery of Marine Fishes
letters to nature sulphide complexes, indicating that Cu sulphide clusters are more 7. Al-Farawati, R. & van den Berg, C. M. G. Metal-sulfide complexation in seawater. Mar. Chem. 63, 331–352 (1999). stable than Cu organic complexes. This explains why laboratory 8. Luther III, G. W., Rickard, D. T., Theberge, S. M. & Olroyd, A. Determination of metal (bi)sulfide cultures of oceanic phytoplankton have been observed to increase stability constants of Mn2+,Fe2+,Co2+,Ni2+,Cu2+, and Zn2+ by voltammetric methods. Environ. Sci. the production of total dissolved sulphides when the concentrations Technol. 30, 671–679 (1996). of free Cu and Zn in the culture media were increased22. Although 9. Helz, G. R, Charnock, J. M., Vaughan, D. J. & Garner, C. D. Multinuclearity of aqueous copper and zinc bisulfide complexes—an EXAFS investigation. Geochim. Cosmochim. Acta 57, the data that we report here suggest that metal sulphide formation is 15–25 (1993). a means of detoxifying trace metals for organisms, further toxico- 10. Luther III, G. W., Theberge, S. M. & Rickard, D. T. Evidence for aqueous clusters as intermediates logical studies are needed to quantify the roles both sulphides and during zinc sulfide formation. Geochim. Cosmochim. Acta 19/20, 3159–3169 (1999). ‘natural’ organic ligands play in controlling Cu toxicity in natural 11. Peters, J. W., Lanzilotta, W. N., Lemon, B. J. & Seefeldt, L. C. X-ray crystal structure of the Fe-only hydrogenase (Cpl) from Clostridium pasteurianum to 1.8 angstrom resolution. Science 282, 1853– waters. 1858 (1998). Sulphur complexation may have a dramatic effect on the acute 12. -
Pleuronectidae
FAMILY Pleuronectidae Rafinesque, 1815 - righteye flounders [=Heterosomes, Pleronetti, Pleuronectia, Diplochiria, Poissons plats, Leptosomata, Diprosopa, Asymmetrici, Platessoideae, Hippoglossoidinae, Psettichthyini, Isopsettini] Notes: Hétérosomes Duméril, 1805:132 [ref. 1151] (family) ? Pleuronectes [latinized to Heterosomi by Jarocki 1822:133, 284 [ref. 4984]; no stem of the type genus, not available, Article 11.7.1.1] Pleronetti Rafinesque, 1810b:14 [ref. 3595] (ordine) ? Pleuronectes [published not in latinized form before 1900; not available, Article 11.7.2] Pleuronectia Rafinesque, 1815:83 [ref. 3584] (family) Pleuronectes [senior objective synonym of Platessoideae Richardson, 1836; family name sometimes seen as Pleuronectiidae] Diplochiria Rafinesque, 1815:83 [ref. 3584] (subfamily) ? Pleuronectes [no stem of the type genus, not available, Article 11.7.1.1] Poissons plats Cuvier, 1816:218 [ref. 993] (family) Pleuronectes [no stem of the type genus, not available, Article 11.7.1.1] Leptosomata Goldfuss, 1820:VIII, 72 [ref. 1829] (family) ? Pleuronectes [no stem of the type genus, not available, Article 11.7.1.1] Diprosopa Latreille, 1825:126 [ref. 31889] (family) Platessa [no stem of the type genus, not available, Article 11.7.1.1] Asymmetrici Minding, 1832:VI, 89 [ref. 3022] (family) ? Pleuronectes [no stem of the type genus, not available, Article 11.7.1.1] Platessoideae Richardson, 1836:255 [ref. 3731] (family) Platessa [junior objective synonym of Pleuronectia Rafinesque, 1815, invalid, Article 61.3.2 Hippoglossoidinae Cooper & Chapleau, 1998:696, 706 [ref. 26711] (subfamily) Hippoglossoides Psettichthyini Cooper & Chapleau, 1998:708 [ref. 26711] (tribe) Psettichthys Isopsettini Cooper & Chapleau, 1998:709 [ref. 26711] (tribe) Isopsetta SUBFAMILY Atheresthinae Vinnikov et al., 2018 - righteye flounders GENUS Atheresthes Jordan & Gilbert, 1880 - righteye flounders [=Atheresthes Jordan [D. -
Ÿþø R J a N H a G E N P H D T H E S
MUSCLE GROWTH AND FLESH QUALITY OF FARMED ATLANTIC HALIBUT (HIPPOGLOSSUS HIPPOGLOSSUS) IN RELATION TO SEASON OF HARVEST Ørjan Hagen A Thesis Submitted for the Degree of PhD at the University of St. Andrews 2008 Full metadata for this item is available in the St Andrews Digital Research Repository at: https://research-repository.st-andrews.ac.uk/ Please use this identifier to cite or link to this item: http://hdl.handle.net/10023/642 This item is protected by original copyright Muscle growth and flesh quality of farmed Atlantic halibut (Hippoglossus hippoglossus) in relation to season of harvest. Ørjan Hagen A thesis submitted for the degree of Doctor of Philosophy University of St Andrews St Andrews, July 2008 ii This thesis is dedicated to my family. I could not have managed without their loving support. Thank you so much! iii Acknowledgements Taking a PhD abroad at a highly respected University across the world has been a milestone of my life. I am very proud to have been a PhD student at the University of St Andrews and very grateful to the people helping me reaching my goals. Looking back at the beginning (October 2003) these last few years have been an educational expedition, full of challenges and memories. I have met people from Australia and Taiwan in the east to Canada in the west, wonderful people that I hope to have collaboration with in the future. There are so many to thank, and I would like to start with my supervisor and the head of the “Fish Muscle Research Group” (FMRG), Prof. -
INVERTEBRATE SPECIES in the EASTERN BERING SEA By
Effects of areas closed to bottom trawling on fish and invertebrate species in the eastern Bering Sea Item Type Thesis Authors Frazier, Christine Ann Download date 01/10/2021 18:30:05 Link to Item http://hdl.handle.net/11122/5018 e f f e c t s o f a r e a s c l o s e d t o b o t t o m t r a w l in g o n fish a n d INVERTEBRATE SPECIES IN THE EASTERN BERING SEA By Christine Ann Frazier RECOMMENDED: — . /Vj Advisory Committee Chair Program Head / \ \ APPROVED: M--- —— [)\ Dean, School of Fisheries and Ocean Sciences • ~7/ . <-/ / f a Dean of the Graduate Sch6oI EFFECTS OF AREAS CLOSED TO BOTTOM TRAWLING ON FISH AND INVERTEBRATE SPECIES IN THE EASTERN BERING SEA A THESIS Presented to the Faculty of the University of Alaska Fairbanks in Partial Fulfillment of the Requirements for the Degree of MASTER OF SCIENCE 6 By Christine Ann Frazier, B.A. Fairbanks, Alaska December 2003 UNIVERSITY OF ALASKA FAIRBANKS ABSTRACT The Bering Sea is a productive ecosystem with some of the most important fisheries in the United States. Constant commercial fishing for groundfish has occurred since the 1960s. The implementation of areas closed to bottom trawling to protect critical habitat for fish or crabs resulted in successful management of these fisheries. The efficacy of these closures on non-target species is unknown. This study determined if differences in abundance, biomass, diversity and evenness of dominant fish and invertebrate species occur among areas open and closed to bottom trawling in the eastern Bering Sea between 1996 and 2000. -
Winter Flounder
Maine 2015 Wildlife Action Plan Revision Report Date: January 13, 2016 Pseudopleuronectes americanus (Winter Flounder) Priority 2 Species of Greatest Conservation Need (SGCN) Class: Actinopterygii (Ray-finned Fishes) Order: Pleuronectiformes (Flatfish) Family: Pleuronectidae (Righteye Flounders) General comments: Maine DMR jurisdiction; W Atlantic specialist = LB-GA No Species Conservation Range Maps Available for Winter Flounder SGCN Priority Ranking - Designation Criteria: Risk of Extirpation: NA State Special Concern or NMFS Species of Concern: NA Recent Significant Declines: Winter Flounder is currently undergoing steep population declines, which has already led to, or if unchecked is likely to lead to, local extinction and/or range contraction. Notes: ASMFC Stock Assess, 30yr, and DFO. 2012. Assessment of winter flounder (Pseudopleuronectes americanus) in the southern Gulf of St. Lawrence (NAFO Div. 4T). DFO Can. Sci. Advis. Sec. Sci. Advis. Rep. 2012/016. Regional Endemic: NA High Regional Conservation Priority: Atlantic States Marine Fisheries Commission Stock Assessments: Status: Unstable/Decreasing, Status Comment: Reference: High Climate Change Vulnerability: NA Understudied rare taxa: NA Historical: NA Culturally Significant: NA Habitats Assigned to Winter Flounder: Formation Name Subtidal Macrogroup Name Subtidal Coarse Gravel Bottom Habitat System Name: Coarse Gravel **Primary Habitat** Notes: adult spawning Habitat System Name: Kelp Bed Notes: juvenile Macrogroup Name Subtidal Mud Bottom Habitat System Name: Submerged Aquatic