A BEGINNERS GUIDE to Frog Identification Contents
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Return Rates of Male Hylid Frogs Litoria Genimaculata, L. Nannotis, L
Vol. 11: 183–188, 2010 ENDANGERED SPECIES RESEARCH Published online April 16 doi: 10.3354/esr00253 Endang Species Res OPENPEN ACCESSCCESS Return rates of male hylid frogs Litoria genimaculata, L. nannotis, L. rheocola and Nyctimystes dayi after toe-tipping Andrea D. Phillott1, 2,*, Keith R. McDonald1, 3, Lee F. Skerratt1, 2 1Amphibian Disease Ecology Group and 2School of Public Health, Tropical Medicine and Rehabilitation Sciences, James Cook University, Townsville, Queensland 4811, Australia 3Threatened Species Branch, Department of Environment and Resource Management, PO Box 975, Atherton, Queensland 4883, Australia ABSTRACT: Toe-tipping is a commonly used procedure for mark-recapture studies of frogs, although it has been criticised for its potential influence on frog behaviour, site fidelity and mortality. We com- pared 24 h return rates of newly toe-tipped frogs to those previously toe-tipped and found no evi- dence of a stress response reflected by avoidance behaviour for 3 species: Litoria genimaculata, L. rheocola and Nyctimystes dayi. L. nannotis was the only studied species to demonstrate a greater reaction to toe-tipping than handling alone; however, return rates (65%) in the 1 to 3 mo after mark- ing were the highest of any species, showing that the reaction did not endure. The comparatively milder short-term response to toe-tipping in N. dayi (24% return rate) may have been caused by the species’ reduced opportunity for breeding. Intermediate-term return rates were relatively high for 2 species, L. nannotis and L. genimaculata, given their natural history, suggesting there were no major adverse effects of toe-tipping. Longer-term adverse effects could not be ruled out for L. -
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. -
Reptiles and Amphibians of Otago
Society for Research on Amphibians and Reptiles in New Zealand (SRARNZ) presents Reptiles and Amphibians of Otago Otago is a large (31,251 km2) and lightly populated region of the southern South Island of Aotearoa New Zealand, stretching from the eastern coastline west to the Southern Alps. The earliest humans, of East Polynesian origin, arrived about 700 years ago. The largest settlement today is the coastal city of Dunedin (pop. >127,000), which grew from a Scottish influx in the 1800s. The Otago Regional Council administers the region, and tribal authority (mana whenua) rests with the iwi of Ngāi Tahu. Climates in the Otago region (roughly 45°– leiopelmatid frogs survive elsewhere in 47°S) range from changeable, cool- New Zealand. Two species of introduced temperate conditions near the coast to frogs are present, but there are no the near-continental climates (baking hot crocodilians, salamanders, terrestrial summers, freezing winters) of the interior. snakes or turtles. Marine turtles (mainly The region provides varied habitats for leatherback turtles, Dermochelys coriacea) herp species, including sand-dunes, visit the coastal waters of Otago but do grasslands, shrublands, wetlands, forests, not nest here. rock structures and scree slopes, some occupied to at least 1900 m above sea level. Today’s herpetofauna is dominated by lizards (solely geckos and skinks), including about 10 described species. A further 12 or more undescribed taxa are recognised Otago by tag names for conservation purposes, and we follow that approach here. All lizards in Otago are viviparous and long- lived, and remain vulnerable to ongoing habitat loss and predation by introduced mammals. -
2.07 Frogs and Wetlands
Chapter 2.7 — Frogs and wetlands • 161 2.7 Frogs and wetlands Dr Arthur White Biosphere Environmental Consultants Pty Ltd Australia Abstract Australian frogs are remarkably diverse in their life styles and their use of wetlands. Our understanding of the ecological needs of frogs is incomplete but we do know some of the major requirements for survival, such as the need for clean water, the need for safe foraging areas, the need for shelter from predators and adverse weather conditions, the need for minimal habitat stress (as this increases the susceptibility of frogs to disease). The design of wetlands must take into account these over-riding requirements, plus the specific requirements that are unique to each frog species. In this paper, I refer to the management of the Green and Golden Bell Frog during the establishment of the Sydney Olympic site as an example of sorts of considerations that are required in managing frogs and wetlands. Chapter 2.7 — Frogs and wetlands • 162 Australian Frogs 2. Air pollution: massive amounts of Sulphur Dioxide and Nitrogen Dioxide (and There are about 250 described frog species in other gases) have been released into the Australia (Anstis 2013). This is a surprisingly high atmosphere since the Industrial Revolution. number of frog species for such an arid continent. These gases combine with moisture in the Australian frogs have had to adapt of the vagaries air and create toxic substances that kill frogs, of Australia’s climate and can survive in areas where other animals and plants. In the northern you would not expect them to be. -
Managing Diversity in the Riverina Rice Fields—
Reconciling Farming with Wildlife —Managing diversity in the Riverina rice fields— RIRDC Publication No. 10/0007 RIRDCInnovation for rural Australia Reconciling Farming with Wildlife: Managing Biodiversity in the Riverina Rice Fields by J. Sean Doody, Christina M. Castellano, Will Osborne, Ben Corey and Sarah Ross April 2010 RIRDC Publication No 10/007 RIRDC Project No. PRJ-000687 © 2010 Rural Industries Research and Development Corporation. All rights reserved. ISBN 1 74151 983 7 ISSN 1440-6845 Reconciling Farming with Wildlife: Managing Biodiversity in the Riverina Rice Fields Publication No. 10/007 Project No. PRJ-000687 The information contained in this publication is intended for general use to assist public knowledge and discussion and to help improve the development of sustainable regions. You must not rely on any information contained in this publication without taking specialist advice relevant to your particular circumstances. While reasonable care has been taken in preparing this publication to ensure that information is true and correct, the Commonwealth of Australia gives no assurance as to the accuracy of any information in this publication. The Commonwealth of Australia, the Rural Industries Research and Development Corporation (RIRDC), the authors or contributors expressly disclaim, to the maximum extent permitted by law, all responsibility and liability to any person, arising directly or indirectly from any act or omission, or for any consequences of any such act or omission, made in reliance on the contents of this publication, whether or not caused by any negligence on the part of the Commonwealth of Australia, RIRDC, the authors or contributors. The Commonwealth of Australia does not necessarily endorse the views in this publication. -
Differential Host Susceptibility to Batrachochytrium Dendrobatidis, an Emerging Amphibian Pathogen
Contributed Paper Differential Host Susceptibility to Batrachochytrium dendrobatidis, an Emerging Amphibian Pathogen C. L. SEARLE,∗§ S. S. GERVASI,∗ J. HUA,# J. I. HAMMOND,# R. A. RELYEA,# D. H. OLSON,† AND A. R. BLAUSTEIN∗ ∗Department of Zoology, Oregon State University, Corvallis, OR 97331, U.S.A. #Department of Biological Sciences, University of Pittsburgh, Pittsburgh, PA 15260, U.S.A. †United States Department of Agriculture, Forest Service, Pacific Northwest Research Station, Corvallis, OR 97331, U.S.A. Abstract: The amphibian fungal pathogen Batrachochytrium dendrobatidis (Bd) has received considerable attention due to its role in amphibian population declines worldwide. Although many amphibian species appear to be affected by Bd, there is little information on species-specific differences in susceptibility to this pathogen. We used a comparative experimental approach to examine Bd susceptibility in 6 amphibian species from the United States. We exposed postmetamorphic animals to Bd for 30 days and monitored mortality, feeding rates, and infection levels. In all species tested, Bd-exposed animals had higher rates of mortality than unexposed (control) animals. However, we found differences in mortality rates among species even though the amount of Bd detected on the different species’ bodies did not differ. Of the species tested, southern toads (Anaxyrus terrestris) and wood frogs (Lithobates sylvaticus) had the highest rates of Bd-related mortality. Within species, we detected lower levels of Bd on individuals that survived longer and found that the relationship between body size and infection levels differed among species. Our results indicate that, even under identical conditions, amphibian species differ in susceptibility to Bd. This study represents a step toward identifying and understanding species variation in disease susceptibility, which can be used to optimize conservation strategies. -
Resource Allocation to Reproduction in Animals
Biol. Rev. (2014), 89, pp. 849–859. 849 doi: 10.1111/brv.12082 Resource allocation to reproduction in animals Sebastiaan A. L. M. Kooijman1,∗ and Konstadia Lika2 1Department of Theoretical Biology, VU University Amsterdam, de Boelelaan 1087, 1081 HV Amsterdam, The Netherlands 2Department of Biology, University of Crete, Voutes University Campus, 70013 Heraklion, Crete, Greece ABSTRACT The standard Dynamic Energy Budget (DEB) model assumes that a fraction κ of mobilised reserve is allocated to somatic maintenance plus growth, while the rest is allocated to maturity maintenance plus maturation (in embryos and juveniles) or reproduction (in adults). All DEB parameters have been estimated for 276 animal species from most large phyla and all chordate classes. The goodness of fit is generally excellent. We compared the estimated values of κ with those that would maximise reproduction in fully grown adults with abundant food. Only 13% of these species show a reproduction rate close to the maximum possible (assuming that κ can be controlled), another 4% have κ lower than the optimal value, and 83% have κ higher than the optimal value. Strong empirical support hence exists for the conclusion that reproduction is generally not maximised. We also compared the parameters of the wild chicken with those of races selected for meat and egg production and found that the latter indeed maximise reproduction in terms of κ, while surface-specific assimilation was not affected by selection. We suggest that small values of κ relate to the down-regulation of maximum body size, and large values to the down-regulation of reproduction. We briefly discuss the ecological context for these findings. -
Amphibian Neuropeptides: Isolation, Sequence Determination and Bioactivity
Amphibian Neuropeptides: Isolation, Sequence Determination and Bioactivity A Thesis submitted for the Degree of Doctor of Philosophy in the Department of Chemistry by Vita Marie Maselli B.Sc. (Hons) July 2006 Preface ___________________________________________________________________________________________ Contents Abstract viii Statement of Originality x Acknowledgements xi List of Figures xii List of Tables xv The 20 Common Amino Acids xvi Chapter 1- Amphibians and their Peptides 1 1.1 Amphibian Peptides 1 1.1a Amphibians 1 1.1b The Role of Anuran Peptides 2 1.2 The Pharmacology of Peptides 4 1.2a Neuropeptides 5 1.2b Hormonal Peptides 7 1.2c Antibacterial Peptides 8 1.2d Anticancer Agents 9 1.2e Antifungal Peptides 9 1.2f Antimalarial Peptides 9 1.2g Pheromones 10 1.2h Miscellaneous Peptides 10 1.3 Peptide Biosynthesis 11 1.4 Methodology 12 1.4a Collection of Frog Secretions 12 1.4b Analysis by High Performance Liquid Chromatography 13 1.4c Mass Spectrometry 14 1.4d Q-TOF 2 Hybrid Quadrupole Time of Flight Mass Spectrometer 15 ii Preface ___________________________________________________________________________________________ 1.5 Peptide Sequencing 18 1.5a Positive and Negative Ion Mass Spectrometry 18 1.5b Automated Edman Sequencing 21 1.5c Enzyme Digestion 22 1.5d Determination of the C-terminal End Group 23 1.6 Bioactivity Testing 24 Chapter 2- Studies of Skin Secretions from the Crinia genus 2.1 Introduction 25 2.1a General 25 2.1b Cyclic Peptides 29 2.2 Host-Defence Compounds from Crinia riparia 30 2.2a Results 30 2.2.1a Isolation -
Parasitic Nematodes of Pool Frog (Pelophylax Lessonae) in the Volga Basin
Journal MVZ Cordoba 2019; 24(3):7314-7321. https://doi.org/10.21897/rmvz.1501 Research article Parasitic nematodes of Pool Frog (Pelophylax lessonae) in the Volga Basin Igor V. Chikhlyaev1 ; Alexander B. Ruchin2* ; Alexander I. Fayzulin1 1Institute of Ecology of the Volga River Basin, Russian Academy of Sciences, Togliatti, Russia 2Mordovia State Nature Reserve and National Park «Smolny», Saransk, Russia. *Correspondence: [email protected] Received: Febrary 2019; Accepted: July 2019; Published: August 2019. ABSTRACT Objetive. Present a modern review of the nematodes fauna of the pool frog Pelophylax lessonae (Camerano, 1882) from Volga basin populations on the basis of our own research and literature sources analysis. Materials and methods. Present work consolidates data from different helminthological works over the past 80 years, supported by our own research results. During the period from 1936 to 2016 different authors examined 1460 specimens of pool frog, using the method of full helminthological autopsy, from 13 regions of the Volga basin. Results. In total 9 nematodes species were recorded. Nematode Icosiella neglecta found for the first time in the studied host from the territory of Russia and Volga basin. Three species appeared to be more widespread: Oswaldocruzia filiformis, Cosmocerca ornata and Icosiella neglecta. For each helminth species the following information included: systematic position, areas of detection, localization, biology, list of definitive hosts, the level of host-specificity. Conclusions. Nematodes of pool frog, excluding I. neglecta, belong to the group of soil-transmitted helminthes (geohelminth) and parasitize in adult stages. Some species (O. filiformis, C. ornata, I. neglecta) are widespread in the host range. -
THE AGILE FROG Species Action Plan Rana Dalmatina SUMMARSUMMARSUMMARYYY DOCUMENT
THE AGILE FROG Species Action Plan Rana dalmatina SUMMARSUMMARSUMMARYYY DOCUMENT The agile frog Rana dalmatina is Despite the efforts of these distributed widely throughout much of organisations, the future of Jersey’s southern and central Europe, but is agile frog is still far from secure. The found in only a few northern locations factors which probably played a key including Jersey - the frog is not found role in the frogs decline are still very anywhere else in the British Isles. The much in evidence: Jersey population of the agile frog has been declining in both range and •water quality and quantity, as a result SSSpppecial pointsss ofofof numbers since the early 1900’s. In the of intensive agriculture, are still below inininteresteresteresttt::: 1970’s only seven localities were listed EU standards in many areas; The agile frog is protected where the frog could still be found, and •the continuing alteration, disturbance, under schedule 1 of the by the mid 1980’s this had fallen to and loss of potentially suitable Conservation of Wildlife only two sites. In 1987 one of the amphibian habitat; (Jersey) Law 2000. remaining two populations was lost as a •the growing numbers of predatory result of a lethal spill of agricultural ducks, cats, and feral ferrets. DESCRIPTION pesticide into the breeding pond. The The agile frog Rana dalmatina species is now believed to be confined These and other factors have combined is a European brown frog, to a single vulnerable population in the to reduce the frog population to the growing up to 90 mm (snout south-west of the island. -
Southern Brown Tree Frog
Our Wildlife Fact Sheet Southern Brown Tree Frog Southern Brown Tree Frogs are one of Victoria’s common frog species. Scientific name Litoria ewingi Did you know? The Southern Brown Tree Frog is an agile hunter. It can leap to catch insects in mid flight. Their large sticky toes make them great climbers. Figure 1. Southern Brown Tree Frog metamorphs © A. Houston Female Southern Brown Tree Frogs can lay up to 600 DSE 2008 eggs at a time. Distribution It takes between 12 and 26 weeks for Southern Brown Southern Brown Tree Frogs occur in southern Victoria, tadpoles to turn into frogs. Tasmania and along the south coast of New South Wales. Description They are found across most of southern, central and Southern Brown Tree Frogs grow up to about 50 mm in north-eastern Victoria, but do not occur in the north- length. west corner of the state. In north-central Victoria and in Their colour is true to their name as they are brown on parts of the state’s north-east they are replaced by the their backs. The backs of their thighs are yellowish to closely-related Plains Brown Tree Frog (Litoria bright orange, and they have a white grainy belly. They paraewingi). also have a distinctive white stripe from the eye to their fore-leg. Their skin is smooth with small lumps. They have webbing on their feet that goes half way up their toes while their fingers have no webbing at all. Breeding males have a light brown vocal sac. Diet Southern Brown Tree Frogs feed mainly on flying insects such as mosquitoes, moths and flies. -
Investigations Into the Life History Stages of the Common Frog (Rana Temporaria) Affected by an Amphibian Ranavirus in the United Kingdom
260 AMPHIBIAN DISEASES Herpetological Review, 2013, 44(2), 260–263. © 2013 by Society for the Study of Amphibians and Reptiles Investigations into the Life History Stages of the Common Frog (Rana temporaria) Affected by an Amphibian Ranavirus in the United Kingdom Ranaviruses are emerging infectious disease agents that af- owned land, so in order to maintain confidentiality we are un- fect a wide range of ectothermic and poikilothermic vertebrates: able to provide more detailed location information than is pro- fish, reptiles (including turtles and tortoises) and amphibians vided in Tables 1 and 2. (Ahne et al. 1997; Chinchar et al. 2009; Miller et al. 2011). In the Live tadpoles were transported in a common container in United Kingdom (UK), amphibian ranaviruses began to emerge pond water to the Institute of Zoology, Zoological Society of in the late 1980s and early 1990s in southeast England (Cunning- London, London, UK. Upon arrival, tadpoles were euthanized ham et al. 1996) and manifested as adult mass morbidity and using an overdose of MS-222 (1g/L tricaine methanesulphonate, mortality events (Cunningham et al. 1993; Cunningham et al. Thompson & Joseph Ltd., Norwich, UK) buffered to pH 7.0 with 1996; Drury et al. 1995). sodium bicarbonate. Tissue samples were then dissected out Evidence for local ranavirus outbreaks in the UK have, to and frozen at -80°C for ranavirus screening. In the case of larger date, relied exclusively upon reports of moribund or dead adult tadpoles, tissues included the right anterior quarter of the body, common frogs (e.g. Cunningham et al. 1993; Cunningham et al.