Sonoma-Mendocino Bull Kelp Recovery Plan

Total Page:16

File Type:pdf, Size:1020Kb

Sonoma-Mendocino Bull Kelp Recovery Plan Sonoma-Mendocino Bull Kelp Recovery Plan For Greater Farallones National Marine Sanctuary and California Department of Fish & Wildlife April 2019 i Cover photo credits (top left) S. Lonhart, NOAA (top right) A. Maguire, CDFW (bottom) S. Lonhart, NOAA Citation: Hohman, R., Hutto, S., Catton, C. and F. Koe. 2019. Sonoma-Mendocino Bull Kelp Recovery Plan. Plan for the Greater Farallones National Marine Sanctuary and the California Department of Fish and Wildlife. San Francisco, CA. 166 pp. This work was made possible with support from: ii Kelp Recovery Working Group Members Co-Chairs: Francesca Koe, Greater Farallones National Marine Sanctuary Advisory Council (GFNMS AC) Cynthia Catton, California Department of Fish and Wildlife Members: Sara Allen, National Parks Service, GFNMS AC Tom Bell, University of California Santa Barbara Bob Bertelli, California Sea Urchin Commission Mark Carr, University of California Santa Cruz Cyndi Dawson, Ocean Protection Council Barbara Emley, Pacific Coast Federation of Fishermen’s Associations, GFNMS AC Tom Ford, The Bay Foundation Jan Freiwald, Reef Check Mike Graham, Moss Landing Marine Laboratory Frank Hurd, The Nature Conservancy John Largier, Bodega Marine Lab, GFNMS AC Abby Mohan, GFNMS AC Josh Russo, Waterman’s Alliance, GFNMS AC Sheila Semans, Noyo Center for Marine Science Javier Silva, Sherwood Valley Band of Pomo Indians Bibit Traut, City College of San Francisco, GFNMS AC Suki Waters, WaterTreks Ecotours Technical Advisors: Steve Lonhart, Monterey Bay National Marine Sanctuary Rebecca Flores-Miller, California Department of Fish and Wildlife Staff to the Working Group: Sara Hutto, Greater Farallones Association Jenn Gamurot, Greater Farallones Association Rietta Hohman, Greater Farallones Association iii TABLE OF CONTENTS List of Tables List of Figures Executive Summary 1.0 Introduction ................................................................................................................................. 1 2.0 Background ................................................................................................................................. 2 2.1 Description of the study region ...................................................................................... 2 2.2 Upwelling ....................................................................................................................... 4 2.3 Marine Protected Areas .................................................................................................. 5 2.4 Bull Kelp Forests ............................................................................................................ 6 2.4.1 Range .............................................................................................................. 6 2.4.2 Morphology and Reproduction ....................................................................... 7 2.4.3 Ecosystem Services ......................................................................................... 7 2.4.4 Natural Variability and Abundance of Bull Kelp ........................................... 9 2.5 Problem Background .................................................................................................... 10 3.0 Climatic and Ecological Stressors Contributing to Kelp Forest Loss ....................................... 12 3.1 Persistent Marine Heatwaves ........................................................................................ 13 3.2 Sea Star Wasting Syndrome ......................................................................................... 15 3.3 Purple Sea Urchin Population Increase ........................................................................ 16 3.4 Sea Otter Extirpation .................................................................................................... 18 3.5 Harmful Algal Blooms ................................................................................................. 19 3.6 Anthropogenic Stressors .............................................................................................. 20 4.0 Economic and Cultural Impacts of Kelp Forest Loss ............................................................... 20 5.0 Kelp Recovery Working Group ................................................................................................ 22 5.1 Purpose Statement, Goals and Scope ........................................................................... 22 5.2 Working Group Process and Timeline ......................................................................... 23 6.0 Strategies for Active Kelp Recovery ......................................................................................... 24 6.1 Reduce Grazing Pressure .............................................................................................. 26 6.2 Enhance Kelp ................................................................................................................ 31 7.0 Restoration Site Selection ......................................................................................................... 32 7.1 Strategies to Identify Candidate Regions and Sites for Restoration ............................. 32 7.2 Guidelines for Applying Site Selection Criteria ........................................................... 33 7.3 Methods ........................................................................................................................ 39 iv 7.4 Site Selection Analysis ................................................................................................. 40 7.5 Recommended Priority Regions for Recovery Action ................................................. 82 8.0 Strategies for Monitoring and Research .................................................................................... 84 8.1 Techniques and Limitations .......................................................................................... 85 8.2 Case Studies and Current Research .............................................................................. 89 9.0 Strategies for Community Engagement .................................................................................... 93 9.1 Guidelines to Develop Consistent Messaging and Engage Audiences ......................... 94 9.1.1 Ongoing Community Engagement Efforts .................................................... 98 9.1.2 Opportunities for Public Involvement in Citizen Science ........................... 100 10.0 Integration with Relevant Action Plans .................................................................................. 101 11.0 Conclusion and Next Steps ..................................................................................................... 104 11.1 Establish a Kelp Recovery Project and Network ........................................................ 104 11.1.1 Build on Existing Partnerships .................................................................... 104 11.2 Implement the Strategies ............................................................................................ 105 12.0 References ............................................................................................................................... 107 Appendix A: Working Group Membership ...................................................................................... 115 Appendix B: Working Group Meeting Summaries .......................................................................... 117 Appendix C: Established Partnerships .............................................................................................. 127 Appendix D: Site Selection Criteria Rankings ................................................................................. 128 v List of Tables Table 1. Ecosystem services and functions provided by bull kelp forests (Springer et al. 2010) .............. 10 Table 2. Summary of commercial urchin harvest efforts in 2018 in the AOI. ........................................... 28 Table 3. Descriptions, reasoning and categories for site selection criteria considered by the Working Group. ......................................................................................................................................... 36 Table 4. Rankings used to determine recommendations for priority regions and sites based on selection criteria. ....................................................................................................................................................... 79 Table 5. Sites of economic value to the recreational abalone harvest. Economic value is derived by the reduction per trip in dollars predicted by Reid et al. that would be lost due to the closure of the recreational abalone fishery (2016). .............................................................................................................................. 81 List of Figures Figure 1. Area of Interest (AOI) for the Recovery Plan is the nearshore habitat of Sonoma and Mendocino counties suitable for bull kelp forests (blue line), and area of the coastline that is 206 miles (331 kilometers) long. ..................................................................................................................................... 3 Figure 2. Upwelling is the process by which surface waters are pushed away from the coastline by surface winds and are replaced by cold, nutrient-rich water that wells up from the bottom of the ocean (NOAA). Upwelling is critical for kelp recruitment and growth. ...............................................................................
Recommended publications
  • Regime Shifts in the Anthropocene: Drivers, Risk, and Resilience
    Supplementary Information for Regime Shifts in the Anthropocene: drivers, risk, and resilience by Juan-Carlos Rocha, Garry D. Peterson & Reinette O. Biggs. This document presents a worked example of a regime shift. We first provide a synthesis of the regime shift dynamics and a causal loop diagram (CLD). We then compare the resulting CLD with other regime shifts to make explicit the role of direct and indirect drivers. For each regime shift analyses in this study we did a similar literature synthesis and CLD which are available in the regime shift database. A longer version of this working example and CLDs can be found at www.regimeshifts.org. 1. Kelps transitions Summary. Kelp forests are marine coastal ecosystems located in shallow areas where large macroalgae ecologically engineer the environment to produce a coastal marine environmental substantially different from the same area without kelp. Kelp forests can undergo a regime shift to turf-forming algae or urchin barrens. These shift leads to loss of habitat and ecological complexity. Shifts to turf algae are related to nutrient input, while shifts to urchin barrens are related to trophic-level changes. The consequent loss of habitat complexity may affect commercially important fisheries. Managerial options include restoring biodiversity and installing wastewater treatment plants in coastal zones. Kelps are marine coastal ecosystems dominated by macroalgae typically found in temperate areas. This group of species form submarine forests with three or four layers, which provides different habitats to a variety of species. These forests maintain important industries like lobster and rockfish fisheries, the chemical industry with products to be used in e.g.
    [Show full text]
  • Konar, B., and J.A. Estes. 2003. the Stability of Boundary Regions
    Ecology, 84(1), 2003, pp. 174±185 q 2003 by the Ecological Society of America THE STABILITY OF BOUNDARY REGIONS BETWEEN KELP BEDS AND DEFORESTED AREAS BRENDA KONAR1,2 AND JAMES A. ESTES1 1U.S. Geological Survey and Department of Biology, A-316 Earth and Marine Sciences Building, University of California, Santa Cruz, California 95064 USA Abstract. Two distinct organizational states of kelp forest communities, foliose algal assemblages and deforested barren areas, typically display sharp discontinuities. Mecha- nisms responsible for maintaining these state differences were studied by manipulating various features of their boundary regions. Urchins in the barren areas had signi®cantly smaller gonads than those in adjacent kelp stands, implying that food was a limiting resource for urchins in the barrens. The abundance of drift algae and living foliose algae varied abruptly across the boundary between kelp beds and barren areas. These observations raise the question of why urchins from barrens do not invade kelp stands to improve their ®tness. By manipulating kelp and urchin densities at boundary regions and within kelp beds, we tested the hypothesis that kelp stands inhibit invasion of urchins. Urchins that were ex- perimentally added to kelp beds persisted and reduced kelp abundance until winter storms either swept the urchins away or caused them to seek refuge within crevices. Urchins invaded kelp bed margins when foliose algae were removed but were prevented from doing so when kelps were replaced with physical models. The sweeping motion of kelps over the sea¯oor apparently inhibits urchins from crossing the boundary between kelp stands and barren areas, thus maintaining these alternate stable states.
    [Show full text]
  • Estimated Extent of Urchin Barrens on the East Coast of Northland, New Zealand
    Estimated extent of urchin barrens on the east coast of Northland, New Zealand Vince Kerr and Roger Grace, October 2017 1 Estimated extent of urchin barrens on the east coast of Northland, New Zealand Vince Kerr and Roger Grace, October 2017 Cover Photo: An example of the urchin barren condition taken just south of the Cape Rodney to Okakari Point (Leigh) Marine Reserve at Cape Rodney, showing the greyish bare rock appearance of the urchin barren contrasted with the dark appearance in the aerial view of the algal forests. These photos also demonstrate the typical zonation of macroalgal forests and urchin barrens found in fished areas in northern New Zealand. Photo credit: Nick Shears Keywords: urchin barrens, marine habitat mapping, habitat classification, algal forest health, algal forest restoration, wave exposure, marine reserves, partially protected areas, Northland Citation: Kerr, V.C., Grace, R.V., 2017. Estimated extent of urchin barrens on shallow reefs of Northland’s east coast. A report prepared for Motiti Rohe Moana Trust. Kerr & Associates, Whangarei. Contact the authors: Vince Kerr, Kerr & Associates Phone +64 9 4351518, email: [email protected] Kerr & Associates web site 2 Contents Executive summary ......................................................................................................................................... 4 Client brief ....................................................................................................................................................... 5 Background
    [Show full text]
  • POTENTIAL IMPACTS of KELP FOREST HABITAT RESTORATION ALONG the PALOS VERDES PENINSULA Jeremy T
    POTENTIAL IMPACTS OF KELP FOREST HABITAT RESTORATION ALONG THE PALOS VERDES PENINSULA Jeremy T. Claisse1, Jonathan P. Williams1, Laurel A. Zahn1, Daniel J. Pondella1 & Tom Ford2 1 Vantuna Research Group, Department of Biology, Occidental College, Los Angeles, CA 90041 2 The Bay Foundation, Los Angeles, CA 90045 Urchin barrens and kelp forest habitat Urchin barrens effect the invertebrate, kelp, benthic cover and fish communities restoration We sampled 25 sites in both 2012 and High densities of the unfished purple 2013 (Fig. 1) using a standardized Kelp Community giant kelp urchin (Strongylocentrotus purpuratus) comprehensive community monitoring southern result in ‘‘urchin barrens’’ largely survey protocol (for details see Hamilton et sea palm devoid of macroalgae across 61 ha of al. 2010 PNAS 107:18272-18277 and Claisse et rocky reef along the Palos Verdes al. 2012 PLoS ONE 7:e30290). Sites included Peninsula in southern California (Fig. 1; established kelp forests (green), extent of mapped urchin barrens shown urchin barrens (red) and those adjacent to urchin barrens (grey). We only in red). The study presented here is used data from the 5 m depth zone where most barrens occur. Species- focused on evaluating the potential specific site means were calculated by pooling data over both years. For effects of kelp forest habitat restoration fishes, estimated lengths were converted to weights using length-weight Fig. 4. nMDS plot of the kelp community using square by comparing the differences between relationships. root transformed density and a Bray-Curtis similarity ©Tom Boyd Images 2013 urchin barren and kelp forest habitats. matrix. Significant differences were found among site • We found significant community level differences among site categories (R adonis PERMANOVA: F2,16=8.5, categories in nMDS plots (Fig.
    [Show full text]
  • Southern Sea Otter (Enhydra Lutris Nereis) 5-Year Review
    Southern Sea Otter (Enhydra lutris nereis) 5-Year Review: Summary and Evaluation %- Photo credit: Lilian Carswell/Service U.S. Fish and Wildlife Service Ventura Fish and Wildlife Office Ventura, California September 15, 2015 5-YEAR REVIEW Southern Sea Otter (Enhydra lutris nereis) I. GENERAL INFORMATION Purpose of 5-Year Reviews The U.S. Fish and Wildlife Service (Service) is required by section 4(c)(2) of the Endangered Species Act (Act) to conduct a status review of each listed species at least once every 5 years. The purpose of a 5-year review is to evaluate whether or not the species’ status has changed since it was listed (or since the most recent 5-year review). Based on the 5-year review, we recommend whether the species should be removed from the list of endangered and threatened species, be changed in status from endangered to threatened, or be changed in status from threatened to endangered. Our original listing of a species as endangered or threatened is based on the existence of threats attributable to one or more of the five threat factors described in section 4(a)(l) of the Act, and we must consider these same five factors in any subsequent consideration of reclassification or delisting of a species. In the 5-year review, we consider the best available scientific and commercial data on the species and focus on new information available since the species was listed or last reviewed. If we recommend a change in listing status based on the results of the 5-year review, we must propose to do so through a separate rule-making process defined in the Act that includes public review and comment.
    [Show full text]
  • Bull Kelp (Nereocystic Lutkeana) Restoration and Management in Northern California
    The University of San Francisco USF Scholarship: a digital repository @ Gleeson Library | Geschke Center Master's Projects and Capstones Theses, Dissertations, Capstones and Projects Spring 5-14-2020 Bull Kelp (Nereocystic lutkeana) Restoration and Management in Northern California Olivia Johnson [email protected] Follow this and additional works at: https://repository.usfca.edu/capstone Part of the Marine Biology Commons, Natural Resources and Conservation Commons, Natural Resources Management and Policy Commons, Other Environmental Sciences Commons, Other Plant Sciences Commons, Sustainability Commons, and the Terrestrial and Aquatic Ecology Commons Recommended Citation Johnson, Olivia, "Bull Kelp (Nereocystic lutkeana) Restoration and Management in Northern California" (2020). Master's Projects and Capstones. 1035. https://repository.usfca.edu/capstone/1035 This Project/Capstone is brought to you for free and open access by the Theses, Dissertations, Capstones and Projects at USF Scholarship: a digital repository @ Gleeson Library | Geschke Center. It has been accepted for inclusion in Master's Projects and Capstones by an authorized administrator of USF Scholarship: a digital repository @ Gleeson Library | Geschke Center. For more information, please contact [email protected]. This Master’s Project Bull Kelp (Nereocystic lutkeana) Restoration and Management in Northern California by Olivia Johnson is submitted in partial fulfillment of the requirements for the degree of: Master of Science in Environmental Management at the University of San Francisco May 10, 2020 Submitted: Received: 5/10/2020 ________________________ Olivia Johnson Date Aviva Rossi Date Table of Contents 1. Introduction…………………………………………………………………………..…….1 1.1. Objectives…..…………………………………………………………………………4 1.2. Background…..…………………………………………………………………..……4 1.2.1. Ecology and Geographic Distribution of Global Kelp Forests 1.2.2.
    [Show full text]
  • Global Kelp Forest Restoration: Past Lessons, Status, and Future Goals
    Title: Global Kelp Forest Restoration: Past lessons, status, and future goals Running Title: global kelp forest restoration List of Authors: Aaron Eger1*, Ezequiel M. Marzinelli2,3,4, Hartvig Christie5, Camilla W. Fagerli5, Daisuke Fujita6, Alejandra Paola Gonzalez7, Seokwoo Hong8, Jeong Ha Kim8, Lynn Chi Lee9,10, Tristin Anoush McHugh11,12, Gregory N. Nishihara13, Masayuki Tatsumi14, Peter D. Steinberg1, 3, Adriana Vergés1, 3 1 Centre for Marine Science and Innovation & Ecology and Evolution Research Centre, School of Biological, Earth and Environmental Sciences, The University of New South Wales, Sydney, NSW 2052, Australia 2 The University of Sydney, School of Life and Environmental Sciences, Sydney, NSW 2006, Australia 3 Sydney Institute of Marine Science, 19 Chowder Bay Rd, Mosman, NSW 2088, Australia 4 Singapore Centre for Environmental Life Sciences Engineering, Nanyang Technological University, Singapore 637551, Singapore 5 Norwegian Institute for Water Research, Gaustadallèen 21, 0349 Oslo, Norway 6 University of Tokyo Marine Science and Technology, School of Marine Bioresources, Applied Phycology, Konan, Minato-ku, Tokyo, Japan 7 Departamento de Ciencias Ecológicas, Facultad de Ciencias, Universidad de Chile. Las Palmeras 3425, Ñuñoa, Santiago. Chile 8 Department of Biological Sciences, Sungkyunkwan University, Suwon, South Korea 9 Gwaii Haanas National Park Reserve, National Marine Conservation Area Reserve, and Haida Heritage Site, 60 Second Beach Road, Skidegate, Haida Gwaii, British Columbia, V0T 1S1, Canada 10 Canada & School
    [Show full text]
  • Research to Develop and Manage the Sea Urchin Fisheries of NSW and Eastern Victoria
    Research to develop and manage the sea urchin fisheries of NSW and eastern Victoria D.G. Worthington and C.Blount Cronulla Fisheries Centre, P.O. Box 21, Cronulla, NSW, 2230 Australia FRDC Project No. 1999/128 October 2003 NSW Fisheries Final Report Series No. 56 ISSN 1440-3544 Research to develop and manage the sea urchin fisheries of NSW and eastern Victoria D.G. Worthington and C.Blount Cronulla Fisheries Centre, P.O. Box 21, Cronulla, NSW, 2230 Australia FRDC Project No. 1999/128 October 2003 NSW Fisheries Final Report Series No. 56 ISSN 1440-3544 Research to develop and manage the sea urchin fisheries of NSW and eastern Victoria October 2003 Authors: D.G. Worthington and C.Blount Published By: NSW Fisheries Postal Address: PO Box 21, Cronulla NSW 2230 Internet: www.fisheries.nsw.gov.au NSW Fisheries This work is copyright. Except as permitted under the Copyright Act (Cth), no part of this publication may be reproduced by any process, electronic or otherwise, without the specific written permission of the copyright owners. Neither may information be stored electronically in any form whatsoever without such permission. DISCLAIMER Every attempt has been made to provide accurate information in this document. However, no liability attaches to NSW Fisheries or to any organisation or individual concerned with the supply of information or the preparation of this document for any consequences of using the information contained in this document. ISSN 1440-3544 Contents i TABLE OF CONTENTS TABLE OF CONTENTS ...............................................................................................................................
    [Show full text]
  • Recreational Divers of Oregon Proposal for Kelp Forest Preservation in Rocky Subtidal Zones of the Oregon Coast
    Initial Proposal Period Oregon Rocky Habitat Management Strategy FORMAL LETTER to O.P.A.C. Recreational Divers of Oregon Proposal for Kelp Forest Preservation in Rocky Subtidal Zones of the Oregon Coast @NBCNEWS: “With a loss of kelp forests, you're going to have a very, very profound impact on an ecosystem,” said Tristin McHugh, Reef Check California’s North coast regional manager. “It's like losing your redwoods. What would happen if you saw 90 percent of your redwoods drop dead right now?” For McHugh and many others, the biggest problem is awareness. Most people don’t even realize what sort of a catastrophe is happening below the sea surface. “This is the fight of our generation,” she said. “If we can't set ourselves up right now, there's going to be nothing for our kids further down the line." Initial Proposal Period Purple sea urchins predating the last kelp on this reef- completing an ‘urchin barren’ Special Note: In case the matching Proposal submitted 12/31/20 on the SeaSketch website may not meet some Rocky Shores’ Proposal screening criteria, (the ideas herein are really meant for most of the subtidal sites of the Oregon Coast) - we are also submitting this via email as a FORMAL LETTER to OPAC and the Rocky Shores Working Group. Pg. 37 Oregon Territorial Sea Plan: Part Three “Where the desired outcome cannot be met with a site designation proposal, members of the public and interested entities should outline their concern or desired regulatory change in a formal letter to the Ocean Policy Advisory Council.” Contact Information Please fill out the following section with primary contact information for this proposal.
    [Show full text]
  • A Marine Megafaunal Extinction and Its Consequences for Kelp
    A MARINE MEGAFAUNAL EXTINCTION AND ITS CONSEQUENCES FOR KELP FORESTS OF THE NORTH PACIFIC by Cameron David Bullen B.Sc., The University of British Columbia, 2017 A THESIS SUBMITTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF MASTER OF SCIENCE in THE FACULTY OF GRADUATE AND POSTDOCTORAL STUDIES (Resources, Environment and Sustainability) THE UNIVERSITY OF BRITISH COLUMBIA (Vancouver) June 2020 © Cameron David Bullen, 2020 The following individuals certify that they have read, and recommend to the Faculty of Graduate and Postdoctoral Studies for acceptance, the thesis entitled: A Marine Megafaunal Extinction and its Consequences for Kelp Forests of the North Pacific submitted by Cameron David Bullen in partial fulfillment of the requirements for the degree of Master of Science in Resources, Environment and Sustainability Examining Committee: Dr. Kai M.A. Chan, Institute for Resources, Environment, and Sustainability (IRES). University of British Columbia Supervisor Dr. Villy Christensen, Institute for Oceans and Fisheries (IOF). University of British Columbia Supervisory Committee Member Dr. Iain McKechnie, Department of Anthropology. University of Victoria Supervisory Committee Member Dr. Edward Gregr, Institute for Resources, Environment, and Sustainability (IRES). University of British Columbia Supervisory Committee Member Dr. Christopher Harley, Department of Zoology. University of British Columbia Additional Examiner ii Abstract Restoration of lost ecosystem functions and species interactions is increasingly seen as central to addressing the extensive degradation of ecosystems and associated losses of biodiversity and ecosystem services. To be effective, such restoration efforts require an understanding of how ecosystems functioned prior to human-caused extinctions and ecological transformations. Global declines of megafauna, such as the extinction of the Steller’s sea cow, are largely a consequence of human action and likely had significant and widespread ecological impacts.
    [Show full text]
  • Recurrent Destructive Grazing of Successionally Immature Kelp Forests by Green Sea Urchins in Vestfjorden, Northern Norway
    MARINE ECOLOGY PROGRESS SERIES Vol. 123: 95-106, 1995 Published July 20 Mar Ecol Prog Ser I LI P P Recurrent destructive grazing of successionally immature kelp forests by green sea urchins in Vestfjorden, Northern Norway Nils T. Hagen Department of Fisheries and Natural Science. Bode College. N-8002 Bode, Norway ABSTRACT: Outbreak populations of the green sea urchin Strongylocentrotus droebachiensis Miiller caused widespread decimation of the original Laminaria hyperborea (Gunn.) Fosl. kelp forest in Vest- florden, Northern Norway, during the early 1980s. In the follow~ngdecade, some of the resulting urch~n-dominatedbarren grounds reverted to kelp forest, which, after persisting for more than 5 yr, began to be eliminated yet again. Age analysis of annual growth rings in kelp stipes from field sites at V~rayIsland inlcate that the time of initial kelp recovery varied from site to site but took place between 1984 and 1987. The earliest independent observations of localized macrophyte recovery were made in 1984 at the Harbour Pier site, where, by August 1992, the new kelp forest had already been eliminated by recurrent destructive grazing. Sea urchin density inside re-established kelp forests at 3 other sites on Vaer~yIsland was 45 to 75 ind. m-2 in 1992. These urchin populations had significantly aggregated spatial patterns, and recurrent destructive grazing appeared to be mrmnent. This predic- tion was verified in 1993 when barren grounds reappeared at all study sltes. The threshold conditions for initiation of destructive grazing have been approximated by a curve in the aggregation-density plane. Sea urchins in the Vestfjorden area are infected by the recently discovered epizootic endopara- sitic nematode Echinornermella matsi.
    [Show full text]
  • Resource Competition, Space Use and Forage Ecology Of
    RESOURCE COMPETITION, SPACE USE AND FORAGE ECOLOGY OF SEA OTTERS, ENHYDRA LUTR1S, IN SOUTHERN SOUTHEAST ALASKA By Zachary Hoyt RECOMMENDED: Dr. M. Tim Tinker Dr. Franz Mueter Dr. Chr/s Siddon S'* Dr. Ginny Eek Advisory Committee Chair _±u Dr. Franz Mueter Chair, Graduate Program in Fisheries APPROVED: ( & l u ^ ( W AMOK- RESOURCE COMPETITION, SPACE USE AND FORAGE ECOLOGY OF SEA OTTERS, ENHYDRA LUTRIS, IN SOUTHERN SOUTHEAST ALASKA A DISSERTATION Presented to the Faculty of the University of Alaska Fairbanks in Partial Fulfillment of the Requirements for the Degree of DOCTOR OF PHILOSOPHY By Zachary Hoyt, B.S., M.S. Fairbanks, AK December 2015 Abstract The growing sea otter population in southern Southeast Alaska is impacting commercial shellfish, through foraging and expanding in range and abundance except where hunted for subsistence. Sea otters and their prey have coexisted in the North Pacific Ocean for approximately 750,000 years, but due to exploitation of sea otters from the 1770s until 1911, the species became extinct over much of its range, including southern Southeast Alaska. Subsequently, invertebrate species flourished and were commercially targeted in the late 1900s. Sea otters were relocated (n = 106) to southern Southeast Alaska in 1968. In this dissertation, I evaluated this marine mammal-fisheries conflict through multiple approaches. In Chapter 1, I analyzed geoduck clam and red sea urchin abundance surveys (1994-2012) and catch and effort data from commercial Dungeness crab fisheries (1969-2010) to identify interactions between sea otters and commercial shellfish. In Chapter 2, I collected geo-locations from 30 instrumented sea otters (2011-2014) to identify space use and range expansion.
    [Show full text]