Potential Impact of Invasive Anuran Species in Western

Total Page:16

File Type:pdf, Size:1020Kb

Potential Impact of Invasive Anuran Species in Western POTENTIAL IMPACT OF INVASIVE ANURAN SPECIES IN WESTERN NEWFOUNDLAND by © Dion O. Kelly A thesis submitted to The School of Graduate Studies in partial fulfillment of the requirements for the degree of Master of Science Cognitive and Behavioural Ecology Programme Memorial University of Newfoundland March 2016 St. John’s Newfoundland and Labrador ABSTRACT Successful dispersal and establishment of invasive anurans (frogs and toads) may be influenced by competitive exclusion and/or niche differentiation with competing species. I investigated the dispersal of anurans in western Newfoundland using anuran calling surveys and pond-edge visual encounter surveys. The Mink Frog, Lithobates septentrionalis, had dispersed ~50 km northeast from the original (2001) discovery location and ~34 km southwest; displaying spatial separation from Green Frogs, Lithobates clamitans, at landscape and local scales. Visual encounter surveys did not reveal any correlation between adult Mink Frogs and odonate competitors. Additionally, I assessed the impact of varying tadpole densities on removal of epilithic periphyton by providing epilithon covered substrates for American Toad, Anaxyrus americanus, tadpoles raised in laboratory or field enclosures. Higher tadpole densities resulted in smaller tadpoles that removed more periphyton from substrates. As anuran population ranges expand, there may be effects on ecological resources for vertebrate and invertebrate competitors. ii ACKNOWLEDGEMENTS First and foremost, I thank Dr. Ian Warkentin for providing this opportunity to expand my knowledge in the field of ecology; his immeasurable support and guidance has been vital to the completion of this project. Thank you also to the members of my supervisory committee, Dr. Christine Campbell and Dr. Robert Scott, for their invaluable advice and assistance in the project design and analysis. I am particularly appreciative of the funding received from the Wildlife Division, Government of Newfoundland and Labrador and the Natural Sciences and Engineering Research Council of Canada in support of this research. To Jasmine Pinksen and Lindsay Batt, the research assistants, I am extremely grateful for your help in collecting the data. I also extend my gratitude to Wanda Ellsworth, Bobbie-Ann Parsons and Maria Howell, for the laboratory support. I sincerely thank Dr. Schneider, Dr. Erin Fraser and Chris Hammill for the advice provided in statistically analyzing data. The writing of my thesis was made easier by the comments, suggestions and support offered by Hayley Alloway, Nodgra Duhaney, Kathy Unger, and Lester Marshall; special thanks to you all for aiding in the completion of this study. To my parents and family, many thanks. I am immensely grateful to Stephanie Small-Kelly for her unwavering support, encouragement and suggestions in pursuing this Master’s degree. Without you, I would not have been able to complete my degree. Finally I offer a posthumous thank you to Peter Vogel, who started me on this road years ago and provided an initial inspiration. iii Table of Contents ABSTRACT ........................................................................................................................ ii ACKNOWLEDGEMENTS ............................................................................................... iii 1. Introduction and Overview ............................................................................................. 1 1.1. Invasive Species ...................................................................................................... 1 1.2. Anuran Ecological Effects ...................................................................................... 3 1.3. Invasive Anurans in Newfoundland ........................................................................ 5 1.4. Thesis Objectives and Outline ................................................................................ 8 1.5. Co-authorship Statement ....................................................................................... 10 1.6. References ............................................................................................................. 11 2. Initial Dispersal and Habitat Use of Newly Introduced Mink Frogs in Western Newfoundland, Canada ................................................................................................ 18 2.1. Abstract ................................................................................................................. 19 2.2. Introduction ........................................................................................................... 19 2.3. Materials and Methods .......................................................................................... 22 2.3.1. Study Species ............................................................................................... 22 2.3.2. Study Sites ................................................................................................... 23 2.3.3. Sampling Anuran Distribution ..................................................................... 24 2.3.4. Habitat Classification ................................................................................... 25 2.3.5. Statistical Analyses ...................................................................................... 26 2.4. Results ................................................................................................................... 27 2.5. Discussion ............................................................................................................. 31 2.6. Acknowledgements ............................................................................................... 35 2.7. Literature Cited ..................................................................................................... 35 3. Impact of Invasive Eastern American Toad Tadpole Populations on Pond Epilithon in Western Newfoundland ................................................................................................ 49 3.1. Abstract ................................................................................................................. 50 3.2. Introduction ........................................................................................................... 51 3.3. Methods ................................................................................................................. 54 iv 3.3.1. Study Sites and Experimental Setup ............................................................ 54 3.3.2. Growth Rate Assessment ............................................................................. 56 3.3.3. Periphyton Removal .................................................................................... 56 3.3.4. Statistical Analysis ....................................................................................... 57 3.4. Results ................................................................................................................... 58 3.4.1. Growth Rate Analysis .................................................................................. 58 3.4.2. Periphyton Removal .................................................................................... 60 3.5. Discussion ............................................................................................................. 61 3.5.1. Density-Dependent Effects on Tadpole Growth .......................................... 61 3.5.2. Periphyton Biomass Removal by American Toad Tadpoles ....................... 63 3.5.3. Conclusion ................................................................................................... 65 3.6. Acknowledgements ............................................................................................... 65 3.7. References ............................................................................................................. 65 4. Summary ...................................................................................................................... 77 4.1. Anuran Distribution and Ecological Impact ......................................................... 77 4.2. References ............................................................................................................. 82 5. Appendices ................................................................................................................... 88 5.1. Appendix I – Anuran-Odonate Surveys ................................................................ 89 5.1.1. Introduction .................................................................................................. 89 5.1.2. Methods ....................................................................................................... 90 5.1.3. Results.......................................................................................................... 91 5.1.4. Discussion .................................................................................................... 91 5.1.5. References .................................................................................................... 92 5.2. Appendix II - Tables ............................................................................................. 97 v List of Tables Table 2-1. Habitat Variables Recorded at Monitoring Sites ......................................... 47 Table 2-2. Water Quality Data – Manual Calling Surveys (2014).. ............................. 48 Table 3-1. Weekly Water Quality - pH, Dissolved Oxygen (mg/l), Conductivity (µS/cm)
Recommended publications
  • Cravens Peak Scientific Study Report
    Geography Monograph Series No. 13 Cravens Peak Scientific Study Report The Royal Geographical Society of Queensland Inc. Brisbane, 2009 The Royal Geographical Society of Queensland Inc. is a non-profit organization that promotes the study of Geography within educational, scientific, professional, commercial and broader general communities. Since its establishment in 1885, the Society has taken the lead in geo- graphical education, exploration and research in Queensland. Published by: The Royal Geographical Society of Queensland Inc. 237 Milton Road, Milton QLD 4064, Australia Phone: (07) 3368 2066; Fax: (07) 33671011 Email: [email protected] Website: www.rgsq.org.au ISBN 978 0 949286 16 8 ISSN 1037 7158 © 2009 Desktop Publishing: Kevin Long, Page People Pty Ltd (www.pagepeople.com.au) Printing: Snap Printing Milton (www.milton.snapprinting.com.au) Cover: Pemberton Design (www.pembertondesign.com.au) Cover photo: Cravens Peak. Photographer: Nick Rains 2007 State map and Topographic Map provided by: Richard MacNeill, Spatial Information Coordinator, Bush Heritage Australia (www.bushheritage.org.au) Other Titles in the Geography Monograph Series: No 1. Technology Education and Geography in Australia Higher Education No 2. Geography in Society: a Case for Geography in Australian Society No 3. Cape York Peninsula Scientific Study Report No 4. Musselbrook Reserve Scientific Study Report No 5. A Continent for a Nation; and, Dividing Societies No 6. Herald Cays Scientific Study Report No 7. Braving the Bull of Heaven; and, Societal Benefits from Seasonal Climate Forecasting No 8. Antarctica: a Conducted Tour from Ancient to Modern; and, Undara: the Longest Known Young Lava Flow No 9. White Mountains Scientific Study Report No 10.
    [Show full text]
  • Amphibian Abundance and Detection Trends During a Large Flood in a Semi-Arid Floodplain Wetland
    Herpetological Conservation and Biology 11:408–425. Submitted: 26 January 2016; Accepted: 2 September 2016; Published: 16 December 2016. Amphibian Abundance and Detection Trends During a Large Flood in a Semi-Arid Floodplain Wetland Joanne F. Ocock1,4, Richard T. Kingsford1, Trent D. Penman2, and Jodi J.L. Rowley1,3 1Centre for Ecosystem Science, School of Biological, Earth and Environmental Sciences, UNSW Australia, Sydney, New South Wales, 2052, Australia 2Centre for Environmental Risk Management of Bushfires, Institute of Conservation Biology and Environmental Management, University of Wollongong, Wollongong, New South Wales 2522, Australia 3Australian Museum Research Institute, Australian Museum, 6 College St, Sydney, New South Wales 2010, Australia 4Corresponding author, email: [email protected] Abstract.—Amphibian abundance and occupancy are often reduced in regulated river systems near dams, but com- paratively little is known about how they are affected on floodplain wetlands downstream or the effects of actively managed flows. We assessed frog diversity in the Macquarie Marshes, a semi-arid floodplain wetland of conserva- tion significance, identifying environmental variables that might explain abundances and detection of species. We collected relative abundance data of 15 amphibian species at 30 sites over four months, coinciding with a large natural flood. We observed an average of 39.9 ± (SE) 4.3 (range, 0-246) individuals per site survey, over 47 survey nights. Three non-burrowing, ground-dwelling species were most abundant at temporarily flooded sites with low- growing aquatic vegetation (e.g., Limnodynastes tasmaniensis, Limnodynastes fletcheri, Crinia parinsignifera). Most arboreal species (e.g., Litoria caerulea) were more abundant in wooded habitat, regardless of water permanency.
    [Show full text]
  • Environment and Communications Legislation Committee Answers to Questions on Notice Environment Portfolio
    Senate Standing Committee on Environment and Communications Legislation Committee Answers to questions on notice Environment portfolio Question No: 3 Hearing: Additional Estimates Outcome: Outcome 1 Programme: Biodiversity Conservation Division (BCD) Topic: Threatened Species Commissioner Hansard Page: N/A Question Date: 24 February 2016 Question Type: Written Senator Waters asked: The department has noted that more than $131 million has been committed to projects in support of threatened species – identifying 273 Green Army Projects, 88 20 Million Trees projects, 92 Landcare Grants (http://www.environment.gov.au/system/files/resources/3be28db4-0b66-4aef-9991- 2a2f83d4ab22/files/tsc-report-dec2015.pdf) 1. Can the department provide an itemised list of these projects, including title, location, description and amount funded? Answer: Please refer to below table for itemised lists of projects addressing threatened species outcomes, including title, location, description and amount funded. INFORMATION ON PROJECTS WITH THREATENED SPECIES OUTCOMES The following projects were identified by the funding applicant as having threatened species outcomes and were assessed against the criteria for the respective programme round. Funding is for a broad range of activities, not only threatened species conservation activities. Figures provided for the Green Army are approximate and are calculated on the 2015-16 indexed figure of $176,732. Some of the funding is provided in partnership with State & Territory Governments. Additional projects may be approved under the Natinoal Environmental Science programme and the Nest to Ocean turtle Protection Programme up to the value of the programme allocation These project lists reflect projects and funding originally approved. Not all projects will proceed to completion.
    [Show full text]
  • DNR Letterhead
    ATU F N RA O L T R N E E S M O T U STATE OF MICHIGAN R R C A P DNR E E S D MI N DEPARTMENT OF NATURAL RESOURCES CHIG A JENNIFER M. GRANHOLM LANSING REBECCA A. HUMPHRIES GOVERNOR DIRECTOR Michigan Frog and Toad Survey 2009 Data Summary There were 759 unique sites surveyed in Zone 1, 218 in Zone 2, 20 in Zone 3, and 100 in Zone 4, for a total of 1097 sites statewide. This is a slight decrease from the number of sites statewide surveyed last year. Zone 3 (the eastern half of the Upper Peninsula) is significantly declining in routes. Recruiting in that area has become necessary. A few of the species (i.e. Fowler’s toad, Blanchard’s cricket frog, and mink frog) have ranges that include only a portion of the state. As was done in previous years, only data from those sites within the native range of those species were used in analyses. A calling index of abundance of 0, 1, 2, or 3 (less abundant to more abundant) is assigned for each species at each site. Calling indices were averaged for a particular species for each zone (Tables 1-4). This will vary widely and cannot be considered a good estimate of abundance. Calling varies greatly with weather conditions. Calling indices will also vary between observers. Results from the evaluation of methods and data quality showed that volunteers were very reliable in their abilities to identify species by their calls, but there was variability in abundance estimation (Genet and Sargent 2003).
    [Show full text]
  • Mannophryne Olmonae) Catherine G
    The College of Wooster Libraries Open Works Senior Independent Study Theses 2014 A Not-So-Silent Spring: The mpI acts of Traffic Noise on Call Features of The loB ody Bay Poison Frog (Mannophryne olmonae) Catherine G. Clemmens The College of Wooster, [email protected] Follow this and additional works at: https://openworks.wooster.edu/independentstudy Part of the Other Environmental Sciences Commons Recommended Citation Clemmens, Catherine G., "A Not-So-Silent Spring: The mpI acts of Traffico N ise on Call Features of The loodyB Bay Poison Frog (Mannophryne olmonae)" (2014). Senior Independent Study Theses. Paper 5783. https://openworks.wooster.edu/independentstudy/5783 This Senior Independent Study Thesis Exemplar is brought to you by Open Works, a service of The oC llege of Wooster Libraries. It has been accepted for inclusion in Senior Independent Study Theses by an authorized administrator of Open Works. For more information, please contact [email protected]. © Copyright 2014 Catherine G. Clemmens A NOT-SO-SILENT SPRING: THE IMPACTS OF TRAFFIC NOISE ON CALL FEATURES OF THE BLOODY BAY POISON FROG (MANNOPHRYNE OLMONAE) DEPARTMENT OF BIOLOGY INDEPENDENT STUDY THESIS Catherine Grace Clemmens Adviser: Richard Lehtinen Submitted in Partial Fulfillment of the Requirement for Independent Study Thesis in Biology at the COLLEGE OF WOOSTER 2014 TABLE OF CONTENTS I. ABSTRACT II. INTRODUCTION…………………………………………...............…...........1 a. Behavioral Effects of Anthropogenic Noise……………………….........2 b. Effects of Anthropogenic Noise on Frog Vocalization………………....6 c. Why Should We Care? The Importance of Calling for Frogs..................8 d. Color as a Mode of Communication……………………………….…..11 e. Biology of the Bloody Bay Poison Frog (Mannophryne olmonae)…...13 III.
    [Show full text]
  • Ecology and Pathology of Amphibian Ranaviruses
    Vol. 87: 243–266, 2009 DISEASES OF AQUATIC ORGANISMS Published December 3 doi: 10.3354/dao02138 Dis Aquat Org OPENPEN ACCESSCCESS REVIEW Ecology and pathology of amphibian ranaviruses Matthew J. Gray1,*, Debra L. Miller1, 2, Jason T. Hoverman1 1274 Ellington Plant Sciences Building, Center for Wildlife Health, Department of Forestry Wildlife and Fisheries, Institute of Agriculture, University of Tennessee, Knoxville, Tennessee 37996-4563, USA 2Veterinary Diagnostic and Investigational Laboratory, College of Veterinary Medicine, University of Georgia, 43 Brighton Road, Tifton, Georgia 31793, USA ABSTRACT: Mass mortality of amphibians has occurred globally since at least the early 1990s from viral pathogens that are members of the genus Ranavirus, family Iridoviridae. The pathogen infects multiple amphibian hosts, larval and adult cohorts, and may persist in herpetofaunal and oste- ichthyan reservoirs. Environmental persistence of ranavirus virions outside a host may be several weeks or longer in aquatic systems. Transmission occurs by indirect and direct routes, and includes exposure to contaminated water or soil, casual or direct contact with infected individuals, and inges- tion of infected tissue during predation, cannibalism, or necrophagy. Some gross lesions include swelling of the limbs or body, erythema, swollen friable livers, and hemorrhage. Susceptible amphi- bians usually die from chronic cell death in multiple organs, which can occur within a few days fol- lowing infection or may take several weeks. Amphibian species differ in their susceptibility to rana- viruses, which may be related to their co-evolutionary history with the pathogen. The occurrence of recent widespread amphibian population die-offs from ranaviruses may be an interaction of sup- pressed and naïve host immunity, anthropogenic stressors, and novel strain introduction.
    [Show full text]
  • Hylidae, Anura) and Description of Ocellated Treefrog Itapotihyla Langsdorffii Vocalizations
    Current knowledge on bioacoustics of the subfamily Lophyohylinae (Hylidae, Anura) and description of Ocellated treefrog Itapotihyla langsdorffii vocalizations Lucas Rodriguez Forti1, Roseli Maria Foratto1, Rafael Márquez2, Vânia Rosa Pereira3 and Luís Felipe Toledo1 1 Laboratório Multiusuário de Bioacústica (LMBio) e Laboratório de História Natural de Anfíbios Brasileiros (LaHNAB), Departamento de Biologia Animal, Instituto de Biologia, Universidade Estadual de Campinas, Campinas, São Paulo, Brazil 2 Fonoteca Zoológica, Departamento de Biodiversidad y Biología Evolutiva, Museo Nacional de Ciencias Naturales, CSIC, Madrid, Spain 3 Centro de Pesquisas Meteorológicas e Climáticas Aplicadas à Agricultura (CEPAGRI), Universidade Estadual de Campinas, Campinas, SP, Brazil ABSTRACT Background. Anuran vocalizations, such as advertisement and release calls, are informative for taxonomy because species recognition can be based on those signals. Thus, a proper acoustic description of the calls may support taxonomic decisions and may contribute to knowledge about amphibian phylogeny. Methods. Here we present a perspective on advertisement call descriptions of the frog subfamily Lophyohylinae, through a literature review and a spatial analysis presenting bioacoustic coldspots (sites with high diversity of species lacking advertisement call descriptions) for this taxonomic group. Additionally, we describe the advertisement and release calls of the still poorly known treefrog, Itapotihyla langsdorffii. We analyzed recordings of six males using the software Raven Pro 1.4 and calculated the coefficient Submitted 24 February 2018 of variation for classifying static and dynamic acoustic properties. Accepted 30 April 2018 Results and Discussion. We found that more than half of the species within the Published 31 May 2018 subfamily do not have their vocalizations described yet. Most of these species are Corresponding author distributed in the western and northern Amazon, where recording sampling effort Lucas Rodriguez Forti, should be strengthened in order to fill these gaps.
    [Show full text]
  • South West Queensland QLD Page 1 of 89 21-Jan-11 Species List for NRM Region South West Queensland, Queensland
    Biodiversity Summary for NRM Regions Species List What is the summary for and where does it come from? This list has been produced by the Department of Sustainability, Environment, Water, Population and Communities (SEWPC) for the Natural Resource Management Spatial Information System. The list was produced using the AustralianAustralian Natural Natural Heritage Heritage Assessment Assessment Tool Tool (ANHAT), which analyses data from a range of plant and animal surveys and collections from across Australia to automatically generate a report for each NRM region. Data sources (Appendix 2) include national and state herbaria, museums, state governments, CSIRO, Birds Australia and a range of surveys conducted by or for DEWHA. For each family of plant and animal covered by ANHAT (Appendix 1), this document gives the number of species in the country and how many of them are found in the region. It also identifies species listed as Vulnerable, Critically Endangered, Endangered or Conservation Dependent under the EPBC Act. A biodiversity summary for this region is also available. For more information please see: www.environment.gov.au/heritage/anhat/index.html Limitations • ANHAT currently contains information on the distribution of over 30,000 Australian taxa. This includes all mammals, birds, reptiles, frogs and fish, 137 families of vascular plants (over 15,000 species) and a range of invertebrate groups. Groups notnot yet yet covered covered in inANHAT ANHAT are notnot included included in in the the list. list. • The data used come from authoritative sources, but they are not perfect. All species names have been confirmed as valid species names, but it is not possible to confirm all species locations.
    [Show full text]
  • Origin of the Parasites of an Invading Species, the Australian Cane Toad (Bufo Marinus): Are the Lungworms Australian Or American?
    Molecular Ecology (2008) 17, 4418–4424 doi: 10.1111/j.1365-294X.2008.03922.x FASTBlackwell Publishing Ltd TRACK Origin of the parasites of an invading species, the Australian cane toad (Bufo marinus): are the lungworms Australian or American? SYLVAIN DUBEY and RICHARD SHINE School of Biological Sciences A08, University of Sydney, Sydney, NSW 2006 Australia Abstract Phylogeographical analyses that identify the geographical origin of parasites in invading species can clarify the parasites’ potential for biological control of the invader and the risks posed by the parasite to native species. Our data on nuclear and mitochondrial genetic sequences show that the nematode lungworms (Rhabdias spp.) in invasive Australian populations of cane toads (Bufo marinus) are Rhabdias pseudosphaerocephala, a South American species. We did not find this lungworm species in any Australian frogs sympatric with cane toads, suggesting that the parasite does not attack Australian frogs and hence may offer potential as a biocontrol agent of the toad. Keywords: amphibians, invasive species, mitochondrial gene, nuclear gene, parasite Received 14 July 2008; revision received 31 July 2008; accepted 7 August 2008 arises if the invader’s parasites are taxa from the introduced Introduction range, because in such cases the lack of host-specificity The process of biological invasion often modifies host- rules out use of the parasite as a biological control, and the parasite relationships. Invasive species may leave some or prior distribution of the parasite means that the invaders’ all of their ancestral (native-range) pathogens behind in the spread will not expose the native fauna to novel pathogens. process of translocation and may be infected by novel Unfortunately, distinguishing whether the parasite of an parasites from the introduced range (Mitchell & Power invading species is itself translocated vs.
    [Show full text]
  • Ecology Assessment Report Lot 2AB132 and 3AB51 Report
    Ecology Assessment Report Lot 2AB132 and 3AB51 Report Release Notice This document is available through the Australia Pacific LNG Upstream Phase 1 Project controlled document system TeamBinder™. The responsibility for ensuring that printed copies remain valid rests with the user. Once printed, this is an uncontrolled document unless issued and stamped Controlled Copy. Third-party issue can be requested via the Australia Pacific LNG Upstream Phase 1 Project Document Control Group. Document Conventions The following terms in this document apply: • Will, shall or must indicate a mandatory course of action • Should indicates a recommended course of action • May or can indicate a possible course of action. Document Custodian The custodian of this document is the Australia Pacific LNG Upstream Phase 1 Project – Environmental Approvals Team Leader. The custodian is responsible for maintaining and controlling changes (additions and modifications) to this document and ensuring the stakeholders validate any changes made to this document. Deviations from Document Any deviation from this document must be approved by the Australia Pacific LNG Upstream Phase 1 Project – Environmental Approvals Team Leader. Doc Ref: Q-4200-15-RP-1002 Revision: 0 Page 2 of 90 Approvals, Land & Stakeholder Team, Australia Pacific LNG Upstream Phase 1 Uncontrolled when printed unless issued and stamped Controlled Copy. Ecology Assessment Report Lot 2AB132 and 3AB51 Report Table of Contents 1. Definitions & Abbreviations ......................................................................................
    [Show full text]
  • No Evidence for the 'Rate-Of-Living' Theory Across the Tetrapod Tree of Life
    Received: 23 June 2019 | Revised: 30 December 2019 | Accepted: 7 January 2020 DOI: 10.1111/geb.13069 RESEARCH PAPER No evidence for the ‘rate-of-living’ theory across the tetrapod tree of life Gavin Stark1 | Daniel Pincheira-Donoso2 | Shai Meiri1,3 1School of Zoology, Faculty of Life Sciences, Tel Aviv University, Tel Aviv, Israel Abstract 2School of Biological Sciences, Queen’s Aim: The ‘rate-of-living’ theory predicts that life expectancy is a negative function of University Belfast, Belfast, United Kingdom the rates at which organisms metabolize. According to this theory, factors that accel- 3The Steinhardt Museum of Natural History, Tel Aviv University, Tel Aviv, Israel erate metabolic rates, such as high body temperature and active foraging, lead to organismic ‘wear-out’. This process reduces life span through an accumulation of bio- Correspondence Gavin Stark, School of Zoology, Faculty of chemical errors and the build-up of toxic metabolic by-products. Although the rate- Life Sciences, Tel Aviv University, Tel Aviv, of-living theory is a keystone underlying our understanding of life-history trade-offs, 6997801, Israel. Email: [email protected] its validity has been recently questioned. The rate-of-living theory has never been tested on a global scale in a phylogenetic framework, or across both endotherms and Editor: Richard Field ectotherms. Here, we test several of its fundamental predictions across the tetrapod tree of life. Location: Global. Time period: Present. Major taxa studied: Land vertebrates. Methods: Using a dataset spanning the life span data of 4,100 land vertebrate spe- cies (2,214 endotherms, 1,886 ectotherms), we performed the most comprehensive test to date of the fundamental predictions underlying the rate-of-living theory.
    [Show full text]
  • Quick Guide to Calling Amphibians Reference: Maine’S Amphibians and Reptiles
    Quick Guide to Calling Amphibians Reference: Maine’s Amphibians and Reptiles Spring Peeper (Pseudacris crucifer): One of Maine’s most widespread species and our smallest frog, measuring under an inch and a half, with a dark, imperfect cross or “X” pattern on the back. It has relatively smooth skin and is generally brown to gray with some yellow on the throat. A full chorus of these tiny frogs can be heard up to a half-mile away; each male makes a shrill, pure, high-pitched breeding call. Wood Frog (Rana sylvatica): The first frog to emerge in the spring, the wood frog can tolerate cold and even freezing temperatures for short periods of ©USGS NEARMI time. It has a dark mask over and below each eye ©USGS NEARMI and is otherwise dark red or tan. Wood frogs are widespread in Maine but limit their breeding generally to temporary or vernal pools. The wood frog’s call sounds like the quack of a duck. ©James Hardy ©James Hardy American Toad (Bufo americanus): Maine’s only toad, the American toad has dry, bumpy skin and is largely terrestrial, going in water only to breed and lay eggs. Its call is a high, musical trill that can last 30 seconds or more. Northern Leopard Frog (Rana pipiens): Apparent declines in the population make the northern leopard frog a species of “Special Concern” in the state of Maine. The leopard frog and its close cousin the pickerel frog are the only frogs in Maine with distinct spots. The leopard frog has two to three unevenly spaced rows of irregular oval spots on its back.
    [Show full text]