No Long-Term Effect of Intracoelomic Acoustic Transmitter Implantation on Survival, Growth, and Body Condition of a Long-Lived Stenotherm in the Wild

Total Page:16

File Type:pdf, Size:1020Kb

No Long-Term Effect of Intracoelomic Acoustic Transmitter Implantation on Survival, Growth, and Body Condition of a Long-Lived Stenotherm in the Wild Canadian Journal of Fisheries and Aquatic Sciences No long-term effect of intracoelomic acoustic transmitter implantation on survival, growth, and body condition of a long-lived stenotherm in the wild Journal: Canadian Journal of Fisheries and Aquatic Sciences Manuscript ID cjfas-2020-0106.R1 Manuscript Type: Article Date Submitted by the 17-Sep-2020 Author: Complete List of Authors: Hubbard, Justin; University of Toronto, Ecology and Evolutionary Biology; University of Toronto at Scarborough, Department of Biological Sciences Hickie, Brendan;Draft Environmental and Resource Studies Program, Trent University Bowman, Jeff; Ontario Ministry of Natural Resources and Forestry, Wildlife Research and Monitoring Section Hrenchuk, Lee; International Institute for Sustainable Development, Blanchfield, Paul; Fisheries and Oceans Canada, Freshwater Institute Rennie, Michael; Lakehead University, Biology acoustic telemetry, surgical implantation, long-term, survivorship, Keyword: growth and condition Is the invited manuscript for consideration in a Special Not applicable (regular submission) Issue? : © The Author(s) or their Institution(s) Page 1 of 52 Canadian Journal of Fisheries and Aquatic Sciences 1 No long-term effect of intracoelomic acoustic transmitter implantation on survival, growth, 2 and body condition of a long-lived stenotherm in the wild 3 Justin A. G. Hubbard1,2,6,7*, Brendan E. Hickie1, Jeff Bowman3, Lee E. Hrenchuk2,5, Paul J. 4 Blanchfield2,5, Michael D. Rennie2,4 5 *Corresponding author: Justin A. G. Hubbard1 (email: [email protected]; 6 phone: 416-280-2248; Fax: 416-978-5878) 7 8 1Trent University, School of the Environment, 1600 West Bank Drive. Peterborough, ON Canada 9 K9L 0G2. Brendan E. Hickie (email: [email protected]) 10 2IISD Experimental Lakes Area, 111 LombardDraft Avenue, Suite 325. Winnipeg, Manitoba, Canada 11 R3B 0T4. Lee E. Hrenchuk ([email protected]), Michael D. Rennie ([email protected]) 12 3Ontario Ministry of Natural Resources and Forestry, Wildlife Research and Monitoring Section, 13 Trent University DNA Building, 1600 West Bank Drive. Peterborough, ON, K9J 7B8. 14 Jeff Bowman (email: [email protected]) 15 4Lakehead University, Department of Biology, 955 Oliver Rd. Thunder Bay, ON, P7B 5E1 16 5Fisheries and Oceans Canada, Freshwater Institute, 501 University Crescent. Winnipeg, MB, 17 R3T 2N6. Paul J. Blanchfield (email: [email protected]) 18 1 Present Affiliations: 6University of Toronto, Department of Ecology and Evolutionary Biology, 25 Willcocks Street, Room 3055, Toronto, Ontario, Canada M5S 3B2 7University of Toronto Scarborough, Department of Biological Sciences, 1265 Military Trail Toronto, Ontario. M1C 1A4 1 © The Author(s) or their Institution(s) Canadian Journal of Fisheries and Aquatic Sciences Page 2 of 52 19 Abstract 20 A fundamental assumption of biotelemetry studies is that there are no adverse 21 consequences from the surgical implantation or presence of the acoustic transmitter. In 22 fisheries, most studies have evaluated this assumption over only short time periods (<2 y) in a 23 laboratory setting. Here we compared the survival, growth, and body condition of populations 24 of Lake Trout (Salvelinus namaycush) in three lakes containing tagged and untagged individuals 25 over a 12-year period (2002-2013). We found no significant negative effects of acoustic 26 telemetry tagging on the long-term survival of fish (estimates of combined annual survival 27 ranged from 67% to 91%), and no negative effect of surgical implantation on growth or body 28 condition for fish of either sex. Additionally,Draft we found no significant effect of transmitter:fish 29 mass ratio on fish survival, growth (with the exception of smaller-bodied fish in one lake), or 30 condition. All implanted fish received tags weighing <1.25% of their mass (in water), indicating 31 that this criterion is desirable for larger-bodied adult Lake Trout. Our findings support the 32 assumption that long-lived fish species tagged with acoustic transmitters via intracoelomic 33 surgery survive, grow, and maintain body condition similar to un-tagged conspecifics over the 34 long-term in the wild. 35 36 Keywords: acoustic telemetry, surgical implantation, long-term, survivorship, growth and 37 condition 2 © The Author(s) or their Institution(s) Page 3 of 52 Canadian Journal of Fisheries and Aquatic Sciences 38 Introduction 39 Biotelemetry can provide novel insights into the spatial ecology and survival rates of 40 aquatic animal populations that were previously impossible to observe in the wild (Hussey et al. 41 2015). Biotelemetry has many uses in fisheries research including applications in studies of fish 42 movement and migration (Keefer et al. 2008; Fielder et al. 2020), anthropogenic impacts on 43 survival and mortality rates in exploited stocks (Donaldson et al. 2008), spatial and temporal 44 habitat use (Charles et al. 2017), and fish behaviour (Johnson et al. 2010). Application of 45 biotelemetry to fisheries research has been occurring for more than half a century (Baras 1991; 46 Cooke et al. 2013), but in recent decades, there has been a dramatic increase in the use of 47 acoustic telemetry in fisheries researchDraft due to the technological advancements (e.g., increased 48 battery life, signal strength and miniaturization) and increasing affordability of the equipment 49 (Kessel et al. 2014). Acoustic telemetry transmitters (hereafter tags) are typically externally 50 attached or internally implanted, although intracoelomic surgical implantation is the most 51 common approach (Jepsen et al. 2002; Bridger and Booth 2003; Brown et al. 2011). 52 A critical assumption of biotelemetry studies is that tagged (i.e., fish implanted with an 53 acoustic tag in the coelom) fish are representative of their populations (Rogers and White 54 2007). Violations of this assumption could lead to spurious findings that are not representative 55 of the studied fish populations but rather associated with the impacts of tagging. Documented 56 negative impacts of capture, handling, and surgical implantation of tags include inflammation 57 (Thorstad et al. 2000), reduced growth over short periods (ca. 5 mo.; Jepsen et al. 2008), 58 decreased swimming ability, altered behaviour (Zale et al. 2005), and increased mortality rates 59 (Brown et al. 2013; Jepsen et al. 2015). Larger tag:fish mass ratios have been shown to amplify 3 © The Author(s) or their Institution(s) Canadian Journal of Fisheries and Aquatic Sciences Page 4 of 52 60 the effects of tagging (Jepsen et al. 2005). The general rule of using a tag weight no larger than 61 1.25% of the fish weight in water (or 2% for tag weight in air; Winter 1983) was largely accepted 62 among researchers, but recent studies have indicated more species- and context-specific 63 approaches to tag size should be considered (Brown et al. 1999; Jepsen et al. 2002; McCabe et 64 al. 2019). By tailoring the most suitable procedures to the specific fish species and research 65 project objectives, many of these impacts can be mitigated over short time scales (Jepsen et al. 66 2002). 67 A challenge for fisheries research remains in understanding the long-term effects of 68 intracoelomic tag implantation (Cooke et al. 2011). Tags are routinely surgically implanted in 69 species known to live for years (e.g., SmallmouthDraft Bass Micropterus dolomieu), decades (e.g., 70 Lake Trout Salvelinus namaycush) or more than a century (e.g. Lake Sturgeon Acipenser 71 fulvescens). Thus, the lifespan of many freshwater fishes is well beyond the battery life of a tag 72 or the duration of a given telemetry study, yet an implanted tag will remain with a fish for its 73 entire life. Lake Trout are a long-lived (50+ y; Schram and Fabrizio 1998), cold-water species 74 that is sensitive to human disturbances for which telemetry studies have played an important 75 role in conservation efforts for decades, especially in the Laurentian Great Lakes (Riley et al. 76 2014; Binder et al. 2017, 2018). As for other fish species, acoustic telemetry studies have been 77 instrumental in improving our understanding of the ecology, life history and habitat use of Lake 78 Trout (Guzzo et al. 2016; Gallagher et al. 2019; Klinard et al. 2019), and in some smaller inland 79 lakes, monitoring of telemetry-tagged Lake Trout has been ongoing for almost two decades 80 (Blanchfield et al. 2005; Guzzo et al. 2017). However, more important than study duration (i.e. 81 period when tags are active) is the consideration of long-term fish welfare, given that fish will 4 © The Author(s) or their Institution(s) Page 5 of 52 Canadian Journal of Fisheries and Aquatic Sciences 82 carry implanted tags for the rest of their lives. Despite this, most tagging effects studies occur in 83 laboratory settings and last for short durations of several weeks to months (e.g. Thorstad et al. 84 2000; Berejikian et al. 2007; Darcy et al. 2019). Potential long-term effects of tags could 85 negatively impact estimates growth, survival, movement, and behaviour from study 86 populations and are thus important to quantify but are currently unknown. 87 The objective of our study was to assess the long-term lethal or sub-lethal effects of 88 surgically implanted acoustic telemetry tags on adult Lake Trout within their natural habitat. 89 Here we compare data from two complementary long-term studies of Lake Trout populations 90 ongoing in several small boreal lakes. Data from an annual population monitoring program 91 were used to compare survival, growthDraft and condition of Lake Trout that only experienced 92 handling in this standard mark-recapture program to Lake Trout that were acoustically tagged 93 in these same lakes (Guzzo et al. 2017). We also examined the effects of tag:fish mass ratio on 94 growth and body condition. Given the documented potential for negative effects of acoustic 95 telemetry tagging on fish survival (Brown et al. 2013) and growth (Jepsen et al.
Recommended publications
  • Long-Term Influence of Climate and Experimental Eutrophication Regimes on Phytoplankton 4 Blooms 5 6 7 Kateri R
    bioRxiv preprint doi: https://doi.org/10.1101/658799; this version posted June 3, 2019. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 1 Article type: Letter 2 3 Long-term influence of climate and experimental eutrophication regimes on phytoplankton 4 blooms 5 6 7 Kateri R. Salk1, Jason J. Venkiteswaran2, Raoul-Marie Couture3, Scott N. Higgins4, Michael J. 8 Paterson4, and Sherry L. Schiff5 9 10 1Nicholas School of the Environment, Duke University, Durham, North Carolina, USA 11 2Department of Geography and Environmental Studies, Wilfrid Laurier University, Ontario, 12 Canada 13 3Department of Chemistry, Université Laval, Quebec, Canada 14 4IISD Experimental Lakes Area Inc., Manitoba, Canada 15 5Department of Earth and Environmental Sciences, University of Waterloo, Ontario, Canada 16 17 18 Corresponding author: 19 Kateri Salk 20 [email protected] 21 Nicholas School of the Environment 22 Duke University 23 Durham, NC 27708 24 USA 25 26 Author Contribution Statement 27 KRS conducted modeling and analysis efforts. RMC provided expertise on model application 28 and validation. SLS and JJV provided guidance on the research questions. KRS, RMC, JJV, and 29 SLS analyzed model fit, guided scenario analysis, and provided interpretations of results. SNH 30 and MJP provided guidance on historical data analyses, model input data, and postprocessing 31 analyses. KRS wrote the manuscript, and all coauthors contributed edits to the manuscript. 32 1 bioRxiv preprint doi: https://doi.org/10.1101/658799; this version posted June 3, 2019.
    [Show full text]
  • David W. Schindler (1940–2021): Trailblazing Scientist and Advocate for the Environment RETROSPECTIVE Karen A
    RETROSPECTIVE David W. Schindler (1940–2021): Trailblazing scientist and advocate for the environment RETROSPECTIVE Karen A. Kidda,1, William F. Donahueb, Erin N. Kellyc, Peter R. Leavittd, and Heidi Swansonc On March 4th, 2021, the global aquatic sciences com- munity lost one of its most influential scientists, David W. Schindler. Dave’s landmark research that led to bet- ter protection of fresh waters around the world, his un- canny ability to identify, raise the profile of, and address key crises in aquatic sciences, and his tireless education of the public and decision makers on environmental issues have left an unmatched legacy. Throughout his monumental career, Dave’s research shone a light on the ecological crises unfolding in fresh- water ecosystems. His trailblazing approach included listening to those who were closest to the environment or a problem he was working on, particularly the wisdom of Indigenous knowledge holders, applying science in a way that was respectful of Indigenous ways of know- ing, and using research findings and his own reputa- tion to amplify their voices and effect more holistic stewardship. Much to the chagrin of some politicians and industries, Dave’s remarkable scientific acumen was matched by his tireless commitment and formida- ble ability to raise public awareness of environmental issues. For him, fresh waters had to be protected, and to do so, science had to be communicated: it was this moral conscience and modus operandi that under- pinned Dave’s decades of effecting real-world change. For many years, he was the most quoted Canadian ac- ademic in the media, a measure of his unwavering com- mitment to putting science in the public eye and one that was recognized with the Royal Canadian Institute’s David W.
    [Show full text]
  • Nutrients, Eutrophication and Harmful Algal Blooms Along the Freshwater to Marine Continuum
    Received: 18 April 2019 Revised: 22 June 2019 Accepted: 2 July 2019 DOI: 10.1002/wat2.1373 OVERVIEW Nutrients, eutrophication and harmful algal blooms along the freshwater to marine continuum Wayne A. Wurtsbaugh1 | Hans W. Paerl2 | Walter K. Dodds3 1Watershed Sciences Department, Utah State University, Logan, Utah Abstract 2Institute of Marine Sciences, University of Agricultural, urban and industrial activities have dramatically increased aquatic North Carolina at Chapel Hill, Morehead nitrogen and phosphorus pollution (eutrophication), threatening water quality and City, North Carolina biotic integrity from headwater streams to coastal areas world-wide. Eutrophication 3Division of Biology, Kansas State creates multiple problems, including hypoxic “dead zones” that reduce fish and University, Manhattan, Kansas shellfish production; harmful algal blooms that create taste and odor problems and Correspondence threaten the safety of drinking water and aquatic food supplies; stimulation of Wayne A. Wurtsbaugh, Watershed Sciences Department, Utah State University, Logan, greenhouse gas releases; and degradation of cultural and social values of these Utah 94322-5210. waters. Conservative estimates of annual costs of eutrophication have indicated $1 Email: [email protected] billion losses for European coastal waters and $2.4 billion for lakes and streams in Funding information the United States. Scientists have debated whether phosphorus, nitrogen, or both NSF Konza LTER, Grant/Award Numbers: need to be reduced to control eutrophication along the freshwater to marine contin- NSF OIA-1656006, NSF DEB 1065255; uum, but many management agencies worldwide are increasingly opting for dual Dimensions of Biodiversity, Grant/Award Numbers: 1831096, 1240851; US National control. The unidirectional flow of water and nutrients through streams, rivers, Science Foundation, Grant/Award Numbers: lakes, estuaries and ultimately coastal oceans adds additional complexity, as each CBET 1230543, 1840715, OCE 9905723, of these ecosystems may be limited by different factors.
    [Show full text]
  • LEE HRENCHUK BIOLOGIST, IISD Experimental Lakes Area
    LEE HRENCHUK BIOLOGIST, IISD Experimental Lakes Area Lee is part of the fish crew at IISD-ELA. Her research focuses on monitoring and assessing the effects of a variety of environmental perturbations (including mercury deposition, cage aquaculture, endocrine disrupting chemicals, eutrophication and climate change) on fish ecology and behaviour in small, oligotrophic lakes in the boreal shield. Lee conducted aquatic field research in both the Canadian Arctic and in Antarctica before settling more permanently at IISD-ELA. Post-graduate studies included examining the accumulation of mercury in yellow perch as part of the whole-lake Mercury Experiment to Assess Atmospheric Loading In Canada and the United States (METAALICUS) at ELA. Lee is an advocate for communicating science to a broader audience and has volunteered with Fort Whyte Alive, the Manitoba Museum and Fisheries and Oceans Canada to talk about scientific ideas and environmental issues with the public. Employment Biologist (IISD Experimental Lakes Area Inc.) Supervisors: Dr. Michael Paterson, Dr. Vince Palace April 2014 to present When IISD Experimental Lakes Area (IISD-ELA) took over operation of ELA from Fisheries and Oceans Canada, I chose to leave my position with DFO and continue my research program with IISD-ELA. My experience and responsibilities at IISD-ELA are much the same as they were with DFO, conducting scientific research to assess the impacts of whole-ecosystem experiments on fish ecology and behaviour at IISD-ELA. My research has focused on monitoring the effects of a variety of environmental perturbations (including mercury deposition, cage aquaculture, endocrine disrupting chemicals, eutrophication, and climate change) on fish in small, oligotrophic lakes in the boreal shield.
    [Show full text]
  • The Atmosphere Submodel for the Assessment of Canada's Nuclear
    } * AECL CA9400058 ~ AECL Research EACL Recherche AECL-9889, COG-91-199 The Atmosphere Submodel for the Assessment of Canada's Nuclear Fuel Waste Management Concept Le sous-modele d'atmosphere pour revaluation du concept du Programme canadien de gestion des dechets de combustible nucleaire B.D. Amiro September 1992 septembre AECL RESEARCH THE ATMOSPHERE SUBMODEL FOR THE ASSESSMENT OF CANADA'S NUCLEAR FUEL WASTE HANAGEMEKT CONCEPT by 8.D. Aniro Whiteshell Laboratories Pinawa, Manitoba ROE 1L0 1992 AECL-9889 COG-91-199 LE SOUS-MODÈLE D'ATMOSPHÈRE POUR L'ÉVALUATION DU CONCEPT DU PROGRAMME CANADIEN DE GESTION DES DÉCHETS DE COMBUSTIBLE NUCLÉAIRE par B.D. Amlro RÉSUMÉ Dans le cadre du Programme canadien de gestion des déchets de combustible nucléaire, on fait de la recherche sur un concept de stockage permanent des déchets de combustible nucléaire immobilisés dans une enceinte creusée à grande profondeur dans la roche plutonlque stable. Quand les barrières de protection auront fini par se rompre dans un avenir lointain, des nucléides radioactifs et chimiquement toxiques, entraînés par les eaux souterraines, pourraient migrer de l'enceinte à la biosphère. Ils pourraient parcourir un cycle dans les eaux superficielles, le sol, l'atmosphère et la chaîne alimentaire. Entre autres, le programme vise à évaluer le mouvement des nucléides par des techniques de modélisation pour calculer la dose radio- logique aux êtres humains et la concentration de contaminants dans 1'environnement. Afin d'atteindre ces objectifs, on a réalisé un modèle de biosphère com- portant quatre sous-modèles. On décrit dans ce rapport le sous-modèle d'atmosphère et les voies par lesquelles les nucléides pourraient traverser l'atmosphère.
    [Show full text]
  • Yukon and Kuskokwim Whitefish Strategic Plan
    U.S. Fish & Wildlife Service Whitefish Biology, Distribution, and Fisheries in the Yukon and Kuskokwim River Drainages in Alaska: a Synthesis of Available Information Alaska Fisheries Data Series Number 2012-4 Fairbanks Fish and Wildlife Field Office Fairbanks, Alaska May 2012 The Alaska Region Fisheries Program of the U.S. Fish and Wildlife Service conducts fisheries monitoring and population assessment studies throughout many areas of Alaska. Dedicated professional staff located in Anchorage, Fairbanks, and Kenai Fish and Wildlife Offices and the Anchorage Conservation Genetics Laboratory serve as the core of the Program’s fisheries management study efforts. Administrative and technical support is provided by staff in the Anchorage Regional Office. Our program works closely with the Alaska Department of Fish and Game and other partners to conserve and restore Alaska’s fish populations and aquatic habitats. Our fisheries studies occur throughout the 16 National Wildlife Refuges in Alaska as well as off- Refuges to address issues of interjurisdictional fisheries and aquatic habitat conservation. Additional information about the Fisheries Program and work conducted by our field offices can be obtained at: http://alaska.fws.gov/fisheries/index.htm The Alaska Region Fisheries Program reports its study findings through the Alaska Fisheries Data Series (AFDS) or in recognized peer-reviewed journals. The AFDS was established to provide timely dissemination of data to fishery managers and other technically oriented professionals, for inclusion in agency databases, and to archive detailed study designs and results for the benefit of future investigations. Publication in the AFDS does not preclude further reporting of study results through recognized peer-reviewed journals.
    [Show full text]
  • IISD Experimental Lakes Area the World’S Freshwater Laboratory
    IISD Experimental Lakes Area The World’s Freshwater Laboratory “IISD-ELA is the place for high-impact science. It is unlike any other facility for its ability to answer the big and pressing questions.” —Dr. Karen Kidd, Canada Research Chair, Canadian Rivers Institute and University of New Brunswick In a time of growing populations and a rapidly changing climate, the world is struggling to respond to challenges to their fresh water. These challenges include the impacts of climate change, agricultural runoff, water management, contaminants such as mercury and organic pollutants, and a growing list of new chemical substances. ENTER IISD-ELA: an exceptional natural laboratory comprised of 58 small lakes and their watersheds set aside for scientific research. Located in a remote region of northwestern Ontario, Canada, it is one of the only places in the world where it is possible to conduct experiments on whole ecosystems. By manipulating these small lakes, scientists are able to examine how all aspects of the ecosystem—from the atmosphere to fish populations—respond. Findings of real-world experiments are often much more accurate than those from research conducted at smaller scales, such as in laboratories. For the last 50 years, our unique research approach has influenced billion-dollar decisions of governments and industries. It has generated more cost-effective environmental policies, regulations and management—all in the name of keeping our water clean. Algal Blooms Blanketing our Lakes Changing Climate, Algal blooms occur when too many nutrients enter a body of water, and Changing Lakes algae feed on them. Groundbreaking discoveries at IISD-ELA regarding Our scientists are mimicking which nutrients cause algal blooms led to policy changes around the conditions that could be world that restrict phosphorus entering lakes and rivers.
    [Show full text]
  • IISD Experimental Lakes Area Environmental Science Experience
    IISD-ELA High School Environmental Student Learning Experience Information for Sponsoring Teachers Dear Sponsoring Teacher, Please find below general information about an exceptional science experience you may wish to promote with some of your more capable and deserving students. Sponsoring teacher requirements are discussed in the last section. To meet our goal of providing an extraordinary experience, the organizers require a little of your time and your careful consideration regarding the students you recommend for this opportunity. Pauline Gerrard IISD-ELA Deputy Director Email: [email protected] Phone: 1 204-807-3903 This July 12-24, 2020 marks the sixth annual IISD Experimental Lakes Area Environmental Science Experience. This field course is offered for students who will be entering 11th or 12th grade in the fall of 2020. About the Science and Location The IISD Experimental Lakes Area Environmental Science Research Station (IISD-ELA), located in northwestern Ontario, is an exceptional natural laboratory composed of 58 small lakes and their watersheds set aside for scientific research. It is one of the only places in the world where it is possible to conduct experiments on whole ecosystems. This unique research program has influenced billion-dollar decisions of governments and industries and has generated many cost-effective policies, regulations and management. The science conducted by the world-class researchers at IISD-ELA has resulted in far greater understanding of environmental issues and significantly reduced human impacts on the natural world—think acid rain, eutrophication, mercury poisoning, aquaculture, oil spills and climate change. Worldwide, there is no other environmental research station like IISD-ELA.
    [Show full text]
  • The Experimental Lakes Area
    Nora J. Casson et. al. Field Trip: The Experimental Lakes Area Field trip: The Experimental Lakes Area Nora J. Casson Department of Geography, University of Winnipeg Morgen Burke Department of Geography, University of North Dakota Adrienne Ducharme Department of Geography, University of Winnipeg Brian McGregor Department of Geography, University of Winnipeg Jamie Paterson Department of Geography, University of Winnipeg Joseph Piwowar Department of Geography, University of Regina Kimberly Thomson Department of Geography, University of Winnipeg Nathan Wilson Department of Geography, Lakehead University Gregory Vandeberg Department of Geography, University of North Dakota Introduction the productivity of plants and algae in lakes, but ultimately con- sume dissolved oxygen, leading to poor water quality and fish The Experimental Lakes Area (ELA) began as a Government death. In order to understand this problem, federal scientists of Canada research station in 1968 tasked with investigating in the late 1960s sought out a remote site where lakes could be the causes of and controls on nutrient pollution in lakes. It was purposefully manipulated to assess their responses to environ- established largely in response to growing public awareness of mental stressors. The ELA is located on the Precambrian shield nuisance algal blooms in lakes located close to cities. Through- of northwestern Ontario, 35 km southeast of Kenora, Ontario. out the 1960s, the algal blooms and fish kills in lakes such as It encompasses 58 lakes designated solely for research
    [Show full text]
  • IISD Experimental Lakes Area Facility Day Tours
    IISD Experimental Lakes Area Facility Day Tours We are happy to organize private tours Access to the road is restricted for schools and independently coordinated by the Ontario Ministry for groups of 10 persons or larger. Natural Resources and Forestry (OMNRF), and requires a permit. Please coordinate with your Touring IISD-ELA tour organizer to ensure that all Our standard day tour of the IISD-ELA facility vehicles have an OMNRF permit. begins at 10:00 a.m. and may include: The IISD-ELA site is located at • A welcome presentation that gives an the end of the gravel road, 30 overview of the history of IISD-ELA and our km from the highway. Continue Our road is signed, science. straight on the main road until careful not to miss it. • A tour of our facilities and closest research you arrive. lakes including: discussions of water flow, Arrival water quality and fish sampling; tours of the chemistry and fish labs; a tour of the We ask that you arrive no later than 10:00 am for Environment Canada metrological station; a day tours. Please respect speed limits on our road hands-on netting activity to collect small fish and drive slowly past the meteorological site. We or zooplankton. would rather you be late than drive too quickly. We will meet you in the parking lot upon your arrival. • Lunch at the beach in our camp recreational area. Please pack your own lunch. We ask that Tours are free of charge, you help us to reduce waste by packing your however, as a registered lunch as waste-free as possible.
    [Show full text]
  • Watershed N Export Will Not Be Reduced Proportionally with N Input
    Accounting for N Fixation in Simple Models of Lake N Loading/export A Thesis Presented By Xiaodan Ruan to The Department of Civil and Environmental Engineering in partial fulfillment of the requirements for the degree of Master of Science in Civil and Environmental Engineering in the field of Environmental Engineering Northeastern University Boston, Massachusetts May, 2014 1 Abstract: Coastal eutrophication, an important global environmental problem, is primarily caused by excess N and management efforts consequently focus on lowering watershed N export (e.g. by reducing fertilizer use). Simple quantitative models are needed to evaluate alternative scenarios at the watershed scale. Existing models generally assume that, for a specific lake/reservoir, a constant fraction of N loading is exported downstream. However, N fixation by cyanobacteria may increase when the external N input is reduced, which may change the (effective) fraction of N exported. Here we present a model that incorporates this process. The model is based on a steady-state mass balance with external input, output, loss/retention and N fixation, where the amount fixed is a function of the N/P ratio of the external input (i.e. when N/P is less than a threshold value, N is fixed). Three approaches are used to parameterize and evaluate the model, including microcosm lab experiments, lake field observations/budgets and lake ecosystem models. Our results suggest that N export will not be reduced proportionally with external N input, which needs to be considered when evaluating management scenarios. 2 1. Introduction 1.1. Coastal water eutrophication Eutrophication of coastal waters is an important problem that can result in degradation of water quality, hypoxia, fish kills and harmful algal blooms (HABs).
    [Show full text]
  • Eutrophication of Lakes Cannot Be Controlled by Reducing Nitrogen Input: Results of a 37-Year Whole-Ecosystem Experiment
    Eutrophication of lakes cannot be controlled by reducing nitrogen input: Results of a 37-year whole-ecosystem experiment David W. Schindler*†, R. E. Hecky‡, D. L. Findlay§, M. P. Stainton§, B. R. Parker*, M. J. Paterson§, K. G. Beaty§, M. Lyng§, and S. E. M. Kasian§ *Department of Biological Sciences, University of Alberta, Edmonton, AB, Canada T6G 2E9; ‡Department of Biology, University of Minnesota, Duluth, MN 55812; and §Freshwater Institute, Canadian Department of Fisheries and Oceans, Winnipeg, MB, Canada R3T 2N6 Contributed by David W. Schindler, May 28, 2008 (sent for review March 25, 2008) Lake 227, a small lake in the Precambrian Shield at the Experimental lead to the erroneous conclusion that N inputs must be con- Lakes Area (ELA), has been fertilized for 37 years with constant trolled to reduce eutrophication. These bioassays and the related annual inputs of phosphorus and decreasing inputs of nitrogen to assumptions have led to very expensive mitigation programs in test the theory that controlling nitrogen inputs can control eu- several countries. trophication. For the final 16 years (1990–2005), the lake was Aquatic scientists have often relied on the Redfield ratio to fertilized with phosphorus alone. Reducing nitrogen inputs in- gauge whether nutrient supplies are sufficient. Redfield (14) creasingly favored nitrogen-fixing cyanobacteria as a response by observed that the ratio of carbon:nitrogen:phosphorus in marine the phytoplankton community to extreme seasonal nitrogen lim- phytoplankton was quite constant, with mean ratios by weight of itation. Nitrogen fixation was sufficient to allow biomass to con- Ϸ40:7:1. The Redfield ratio has subsequently been accepted as tinue to be produced in proportion to phosphorus, and the lake a general indicator for balanced growth with potential for near remained highly eutrophic, despite showing indications of extreme optimum growth rates (8).
    [Show full text]