On the Roles of Phylogeny and Stochasticity in The

Total Page:16

File Type:pdf, Size:1020Kb

On the Roles of Phylogeny and Stochasticity in The ON THE ROLES OF PHYLOGENY AND STOCHASTICITY IN THE EVOLUTION OF PERENNIBRANCHIATE TROGLOBITIC SALAMANDERS THOMAS R. JONES' Museum of Zoology, University of Michigan, Ann Arbor, MI 48109 USA; 313-936-0134; Bitnet USERGFTV@UMICHUM; Internet [email protected] and D. BRUCE THOMPSON Department of Zoology, Arizona State University, Tempe, AZ 85287 USA 602-263-1556 Key Words: salamander, troglobitic, paedomorphosis, adaptation, speciation, perennibranchiate Suggested running head: Troglobitic salamander evolution 1 Manuscript corresponding author 1 ABSTRACT Many troglobitic salamanders exhibit paedomorphic morphologies including perennibranchiation, a morphology that has been viewed as a specific adaptation to cave environments. We present a reexamination of that assumption in a phylogenetic context. We suggest that the perennibranchiate condition in troglobitic salamanders is not an adaptation to cave life that has evolved repeatedly and independently, but rather is a consequence of historical, i.e., phylogenetic, processes. Perennibranchiation appears to be a synapomorphy of the clade of hemidactyliine salamanders exclusive of Hemidactylium, and as such has not evolved independently in the obligately troglobitic forms. Further, all known proteid salamanders are perennibranchiate, and therefore that morphology cannot be a specific adaptation in Proteus anquinus. We submit that perennibranchiation in troglobitic salamanders is a result of stochastic "entrapment" of epigean species that were polymorphic (or fixed) for a perennibranchiate condition. Cave-dwelling, perennibranchiate Ambystoma tiqrinum mavortium in south-central New Mexico are an example of a possible intermediate stage in the evolution of obligately troglobitic salamanders. Finally, if a genetic propensity for a perennibranchiate polymorphism exists within a lineage, ecological isolation in caves might be a sufficient condition for further morphological divergence and speciation within that lineage. 2 Recently, there has been a renewed awareness of the important union of ecological and adaptive inference with phylogenetic systematics. While much of the discussion has been necessarily methodological (Brooks, 1985; Coddington, 1988; Brooks and McLennan, 1991), few empirical studies have been directed at particular groups of organisms (e.g., Dunham and Miles, 1985; McLennan et al., 1988; Pearson et al., 1988; Donoghue, 1989; Mooi et al., 1989). This body of work correctly suggests that many commonly held assumptions about adaptation and character evolution should be reexamined in a historical context. Herein we present a case study of the evolution of a perennibranchiate morphology in troglobitic salamanders in such a context. A variety of paedomorphic features may comprise the morphology of troglobitic salamanders (see Wake, 1966), the most notable of which are represented in non-metamorphosing, branchiate adults'. The evolution of perennibranchiate troglobitic salamanders often is discussed implicitly as a deterministic process in which metamorphosing, epigean (surface-dwelling) salamander ancestors enter caves, and descendants subsequently evolve a suite of morphological characteristics, including a perennibranchiate condition, that provide them with a selective advantage in the cave environment. Alternatively, we suggest that a perennibranchiate condition in troglobitic salamanders is a consequence of historical, i.e., phylogenetic, processes rather than an adaptation to cave life, and that the commonness of a perennibranchiate condition in troglobitic salamanders is a result of stochastic "entrapment" of epigean species that are already polymorphic (or fixed) for a perennibranchiate condition. We also provide an example of perennibranchiate, cave-dwelling tiger salamanders (Ambvstoma tiqrinum mavortium), that could represent an intermediate stage in the evolution of obligately troglobitic salamanders. We frame our remarks with respect to 1 In the absence of definitive data describing the developmental evolution of a paedomorphic, perennibranchiate morphology, i.e., neoteny or progenesis (sensu Gould, 1977; Alberch et al., 1979), and to facilitate discussion, we use "perennibranchiate" or "mature branchiate" to refer specifically to sexually mature, permanently gilled salamanders ("perennibranchiation" describes the condition), whether that morphology is considered facultative or obligate. 3 West-Eberhard's (1986, 1989) reviews of the evolutionary significance of alternative phenotypes, and close with a comment regarding general attempts to understand the evolution of perennibranchiate salamanders. TROGLOBITIC TAXA AND HYPOTHESES EXPLAINING PERENNIBRANCHIATE MORPHOLOGY There are six genera of true troglobitic salamanders in two families (Brandon, 1971; see Barr and Holsinger, 1985; Holsinger, 1988 for reviews and definitions) (Table 1.). The tribe Hemidactyliini, family Plethodontidae, includes about ten troglobitic species all North American endemics (taxonomy of some groups is unclear, and is likely to change in the near future; P.T. Chippindale and D.M. Hillis, pers. comm.), while the European proteid, Proteus anquinus, is the only form known elsewhere (Brandon, 1971; Sweet, 1984; Barr and Holsinger, 1985). In North America troglobitic salamanders are found in the Valley and Ridge, adjacent Appalachian Plateau, and Dougherty Plain physiographic provinces (in the southeastern USA), the Ozark Mountains of Arkansas, Missouri, Oklahoma and Kansas, and the Edwards Plateau region, Texas. Perhaps the most obvious feature of troglobitic salamanders is that nearly all species are perennibranchiate; only Gyrinophilus subterraneus and Typhlotriton spelaeus metamorphose. Hypotheses explaining evolution of troglobitic organisms fall generally into two catagories, in which epigean forms either 1) actively enter subterranean systems, either to escape harsh surface environments or to exploit unoccupied niches, or 2) enter caves passively as a result of physical forces beyond their control (see Culver, 1982). Hypotheses in the former category emphasizing escape have been advanced for most troglobitic salamanders (Wake, 1966; Brandon, 1971; Duellman and Trueb, 1986) and terrestrial invertebrates (summaries in Culver, 1982; Holsinger, 1988; Holsinger and Culver, 1988). Mitchell and Smith (1972) extended this theme, suggesting that cave colonizers survived inhospitable climates that removed their epigean relatives. Howarth's (1973, 1981) adaptive-shift theory 4 suggests terrestrial invertebrates actively enter new, ecologically "empty" caves (e.g., lava tubes). In the second category, Sweet (1982, 1984) suggested failure of springs following erosion of their water-bearing strata led to underground retreat of epigean, spring-dwelling salamanders along the edge of the Edwards Plateau, Texas. Similar explanations include entry into caves via springs or stream capture, especially in the case of aquatic invertebrates (Holsinger, 1988; Holsinger and Culver, 1988). A perennibranchiate condition in cave salamanders is framed typically as an adaptive response to cave conditions, although hypothesized selective pressures may vary. For example, Hecht and Edwards (1976:669) said, "Proteus, Typhlomolge, Haideotriton, and other troglobitic salamanders resemble each other in many morphological characters as a result of the severe orthoselective pressures of the cave environment. These resemblances are without question the result of convergent evolution." Here we summarize various hypotheses offered to explain the evolution of perennibranchiates, explicitly in troglobitic salamanders. Wake (1966:82) postulated that within caves, perennibranchiate plethodontids might have had a selective advantage over transforming individuals resulting in eventual fixation of the larval morphology. Dent (1968:303) suggested that selective pressures such as food abundance (in aquatic vs. terrestrial cave environments) likely "brought about the rise of neoteny [sic] in caves." Brandon (1971) also suggested a perennibranchiate morphology was a likely evolutionary response to food requirements and availability, in which morphological features of perennibranchs (e.g., neuromasts, spatulate snouts) allow more efficient feeding in permanently dark, aquatic habitats; this idea also has been emphasized by Culver (1982). In addition, perennibranchs avoid energy expenditures necessary for metamorphosis, which might be important in caves where food is less abundant relative to surface habitats (Brandon, 1971). According to Wilbur and Collins (1973), within caves a selective disadvantage may exist for metamorphosing salamanders that leave stable and relatively productive aquatic habitats to enter unproductive terrestrial environments. 5 Bruce (1976) provided life history data on Eurycea neotenes (as currently recognized, an epigean and troglobitic species) suggesting perennibranchiation evolved through lowering size and age at maturity in response to high juvenile mortality and environmentally determined minimum metamorphic size. Although Bruce (1976) did not implicate cave conditions, Sweet (1977:374) argued against Bruce's suggestions, saying perennibranchiate E. neotenes apparently evolved as a response to "selective disadvantages of metamorphosis" in subsurface aquatic habitats where branchiate animals could feed more effectively. Bruce (1979:1000) later modified and extended Brandon's (1971) ideas regarding perennibranchiate Gyrinophilus palleucus, suggesting the prey resource base was the "relevant environmental
Recommended publications
  • Other Contributions
    Other Contributions NATURE NOTES Amphibia: Caudata Ambystoma ordinarium. Predation by a Black-necked Gartersnake (Thamnophis cyrtopsis). The Michoacán Stream Salamander (Ambystoma ordinarium) is a facultatively paedomorphic ambystomatid species. Paedomorphic adults and larvae are found in montane streams, while metamorphic adults are terrestrial, remaining near natal streams (Ruiz-Martínez et al., 2014). Streams inhabited by this species are immersed in pine, pine-oak, and fir for- ests in the central part of the Trans-Mexican Volcanic Belt (Luna-Vega et al., 2007). All known localities where A. ordinarium has been recorded are situated between the vicinity of Lake Patzcuaro in the north-central portion of the state of Michoacan and Tianguistenco in the western part of the state of México (Ruiz-Martínez et al., 2014). This species is considered Endangered by the IUCN (IUCN, 2015), is protected by the government of Mexico, under the category Pr (special protection) (AmphibiaWeb; accessed 1April 2016), and Wilson et al. (2013) scored it at the upper end of the medium vulnerability level. Data available on the life history and biology of A. ordinarium is restricted to the species description (Taylor, 1940), distribution (Shaffer, 1984; Anderson and Worthington, 1971), diet composition (Alvarado-Díaz et al., 2002), phylogeny (Weisrock et al., 2006) and the effect of habitat quality on diet diversity (Ruiz-Martínez et al., 2014). We did not find predation records on this species in the literature, and in this note we present information on a predation attack on an adult neotenic A. ordinarium by a Thamnophis cyrtopsis. On 13 July 2010 at 1300 h, while conducting an ecological study of A.
    [Show full text]
  • Herpetological Review
    Herpetological Review Volume 41, Number 2 — June 2010 SSAR Offi cers (2010) HERPETOLOGICAL REVIEW President The Quarterly News-Journal of the Society for the Study of Amphibians and Reptiles BRIAN CROTHER Department of Biological Sciences Editor Southeastern Louisiana University ROBERT W. HANSEN Hammond, Louisiana 70402, USA 16333 Deer Path Lane e-mail: [email protected] Clovis, California 93619-9735, USA [email protected] President-elect JOSEPH MENDLELSON, III Zoo Atlanta, 800 Cherokee Avenue, SE Associate Editors Atlanta, Georgia 30315, USA e-mail: [email protected] ROBERT E. ESPINOZA KERRY GRIFFIS-KYLE DEANNA H. OLSON California State University, Northridge Texas Tech University USDA Forestry Science Lab Secretary MARION R. PREEST ROBERT N. REED MICHAEL S. GRACE PETER V. LINDEMAN USGS Fort Collins Science Center Florida Institute of Technology Edinboro University Joint Science Department The Claremont Colleges EMILY N. TAYLOR GUNTHER KÖHLER JESSE L. BRUNNER Claremont, California 91711, USA California Polytechnic State University Forschungsinstitut und State University of New York at e-mail: [email protected] Naturmuseum Senckenberg Syracuse MICHAEL F. BENARD Treasurer Case Western Reserve University KIRSTEN E. NICHOLSON Department of Biology, Brooks 217 Section Editors Central Michigan University Mt. Pleasant, Michigan 48859, USA Book Reviews Current Research Current Research e-mail: [email protected] AARON M. BAUER JOSHUA M. HALE BEN LOWE Department of Biology Department of Sciences Department of EEB Publications Secretary Villanova University MuseumVictoria, GPO Box 666 University of Minnesota BRECK BARTHOLOMEW Villanova, Pennsylvania 19085, USA Melbourne, Victoria 3001, Australia St Paul, Minnesota 55108, USA P.O. Box 58517 [email protected] [email protected] [email protected] Salt Lake City, Utah 84158, USA e-mail: [email protected] Geographic Distribution Geographic Distribution Geographic Distribution Immediate Past President ALAN M.
    [Show full text]
  • Pseudoeurycea Naucampatepetl. the Cofre De Perote Salamander Is Endemic to the Sierra Madre Oriental of Eastern Mexico. This
    Pseudoeurycea naucampatepetl. The Cofre de Perote salamander is endemic to the Sierra Madre Oriental of eastern Mexico. This relatively large salamander (reported to attain a total length of 150 mm) is recorded only from, “a narrow ridge extending east from Cofre de Perote and terminating [on] a small peak (Cerro Volcancillo) at the type locality,” in central Veracruz, at elevations from 2,500 to 3,000 m (Amphibian Species of the World website). Pseudoeurycea naucampatepetl has been assigned to the P. bellii complex of the P. bellii group (Raffaëlli 2007) and is considered most closely related to P. gigantea, a species endemic to the La specimens and has not been seen for 20 years, despite thorough surveys in 2003 and 2004 (EDGE; www.edgeofexistence.org), and thus it might be extinct. The habitat at the type locality (pine-oak forest with abundant bunch grass) lies within Lower Montane Wet Forest (Wilson and Johnson 2010; IUCN Red List website [accessed 21 April 2013]). The known specimens were “found beneath the surface of roadside banks” (www.edgeofexistence.org) along the road to Las Lajas Microwave Station, 15 kilometers (by road) south of Highway 140 from Las Vigas, Veracruz (Amphibian Species of the World website). This species is terrestrial and presumed to reproduce by direct development. Pseudoeurycea naucampatepetl is placed as number 89 in the top 100 Evolutionarily Distinct and Globally Endangered amphib- ians (EDGE; www.edgeofexistence.org). We calculated this animal’s EVS as 17, which is in the middle of the high vulnerability category (see text for explanation), and its IUCN status has been assessed as Critically Endangered.
    [Show full text]
  • About the Book the Format Acknowledgments
    About the Book For more than ten years I have been working on a book on bryophyte ecology and was joined by Heinjo During, who has been very helpful in critiquing multiple versions of the chapters. But as the book progressed, the field of bryophyte ecology progressed faster. No chapter ever seemed to stay finished, hence the decision to publish online. Furthermore, rather than being a textbook, it is evolving into an encyclopedia that would be at least three volumes. Having reached the age when I could retire whenever I wanted to, I no longer needed be so concerned with the publish or perish paradigm. In keeping with the sharing nature of bryologists, and the need to educate the non-bryologists about the nature and role of bryophytes in the ecosystem, it seemed my personal goals could best be accomplished by publishing online. This has several advantages for me. I can choose the format I want, I can include lots of color images, and I can post chapters or parts of chapters as I complete them and update later if I find it important. Throughout the book I have posed questions. I have even attempt to offer hypotheses for many of these. It is my hope that these questions and hypotheses will inspire students of all ages to attempt to answer these. Some are simple and could even be done by elementary school children. Others are suitable for undergraduate projects. And some will take lifelong work or a large team of researchers around the world. Have fun with them! The Format The decision to publish Bryophyte Ecology as an ebook occurred after I had a publisher, and I am sure I have not thought of all the complexities of publishing as I complete things, rather than in the order of the planned organization.
    [Show full text]
  • Molecular Diversification of Salamanders of The
    Blackwell Science, LtdOxford, UKBIJBiological Journal of the Linnean Society0024-4066The Linnean Society of London, 2004? 2004 813 325346 Original Article TROPICAL AMERICAN SALAMANDER DIVERSIFICATION G. PARRA-OLEA ET AL Biological Journal of the Linnean Society, 2004, 81, 325–346. With 7 figures Molecular diversification of salamanders of the tropical American genus Bolitoglossa (Caudata: Plethodontidae) and its evolutionary and biogeographical implications GABRIELA PARRA-OLEA1, MARIO GARCÍA-PARÍS2 and DAVID B. WAKE3* 1Instituto de Biología, UNAM. AP 70–153, CP 04510, Ciudad Universitaria, México D.F., México 2Museo Nacional de Ciencias Naturales, CSIC, José Gutiérrez Abascal, 2, 28006 Madrid, Spain 3Museum of Vertebrate Zoology, University of California, Berkeley, CA 94720–3160, USA Received December 2002; accepted for publication August 2003 The largest genus of salamanders, Bolitoglossa (Plethodontidae), is widespread in tropical America, where it occurs in diverse habitats and elevations, from high elevation grasslands to lowland rain forest. It has the most extensive geographical range of any salamander genus. While most species occur in Middle America, it ranges throughout most of tropical South America as well. Phylogenetic analysis of 1196 bp of two mitochondrial genes (cytochrome b, 16S RNA) from 55 species offers strong support for the monophyly of the genus and sorts the species into a number of clades. Taking into account morphology, distribution, general ecology, and prior systematic and taxonomic studies, we recognize seven subgenera, four of them new: Bolitoglossa Duméril, Bibron et Duméril, 1854, Eladinea Miranda Ribeiro, 1937, Magnadigita Taylor, 1944, Mayamandra, Nanotriton, Oaxakia and Pachymandra. All South American and some lower Middle American species are included in a single well -supported clade, Eladinea.
    [Show full text]
  • I Online Supplementary Data – Sexual Size Dimorphism in Salamanders
    Online Supplementary data – Sexual size dimorphism in salamanders Supplementary data S1. Species data used in this study and references list. Males Females SSD Significant test Ref Species n SVL±SD n SVL±SD Andrias davidianus 2 532.5 8 383.0 -0.280 12 Cryptobranchus alleganiensis 53 277.4±5.2 52 300.9±3.4 0.084 Yes 61 Batrachuperus karlschmidti 10 80.0 10 84.8 0.060 26 Batrachuperus londongensis 20 98.6 10 96.7 -0.019 12 Batrachuperus pinchonii 5 69.6 5 74.6 0.070 26 Batrachuperus taibaiensis 11 92.9±12.1 9 102.1±7.1 0.099 Yes 27 Batrachuperus tibetanus 10 94.5 10 92.8 -0.017 12 Batrachuperus yenyuadensis 10 82.8 10 74.8 -0.096 26 Hynobius abei 24 57.8±2.1 34 55.0±1.2 -0.048 Yes 92 Hynobius amakusaensis 22 75.4±4.8 12 76.5±3.6 0.014 No 93 Hynobius arisanensis 72 54.3±4.8 40 55.2±4.8 0.016 No 94 Hynobius boulengeri 37 83.0±5.4 15 91.5±3.8 0.102 Yes 95 Hynobius formosanus 15 53.0±4.4 8 52.4±3.9 -0.011 No 94 Hynobius fuca 4 50.9±2.8 3 52.8±2.0 0.037 No 94 Hynobius glacialis 12 63.1±4.7 11 58.9±5.2 -0.066 No 94 Hynobius hidamontanus 39 47.7±1.0 15 51.3±1.2 0.075 Yes 96 Hynobius katoi 12 58.4±3.3 10 62.7±1.6 0.073 Yes 97 Hynobius kimurae 20 63.0±1.5 15 72.7±2.0 0.153 Yes 98 Hynobius leechii 70 61.6±4.5 18 66.5±5.9 0.079 Yes 99 Hynobius lichenatus 37 58.5±1.9 2 53.8 -0.080 100 Hynobius maoershanensis 4 86.1 2 80.1 -0.069 101 Hynobius naevius 72.1 76.7 0.063 102 Hynobius nebulosus 14 48.3±2.9 12 50.4±2.1 0.043 Yes 96 Hynobius osumiensis 9 68.4±3.1 15 70.2±3.0 0.026 No 103 Hynobius quelpaertensis 41 52.5±3.8 4 61.3±4.1 0.167 Yes 104 Hynobius
    [Show full text]
  • 3Systematics and Diversity of Extant Amphibians
    Systematics and Diversity of 3 Extant Amphibians he three extant lissamphibian lineages (hereafter amples of classic systematics papers. We present widely referred to by the more common term amphibians) used common names of groups in addition to scientifi c Tare descendants of a common ancestor that lived names, noting also that herpetologists colloquially refer during (or soon after) the Late Carboniferous. Since the to most clades by their scientifi c name (e.g., ranids, am- three lineages diverged, each has evolved unique fea- bystomatids, typhlonectids). tures that defi ne the group; however, salamanders, frogs, A total of 7,303 species of amphibians are recognized and caecelians also share many traits that are evidence and new species—primarily tropical frogs and salaman- of their common ancestry. Two of the most defi nitive of ders—continue to be described. Frogs are far more di- these traits are: verse than salamanders and caecelians combined; more than 6,400 (~88%) of extant amphibian species are frogs, 1. Nearly all amphibians have complex life histories. almost 25% of which have been described in the past Most species undergo metamorphosis from an 15 years. Salamanders comprise more than 660 species, aquatic larva to a terrestrial adult, and even spe- and there are 200 species of caecilians. Amphibian diver- cies that lay terrestrial eggs require moist nest sity is not evenly distributed within families. For example, sites to prevent desiccation. Thus, regardless of more than 65% of extant salamanders are in the family the habitat of the adult, all species of amphibians Plethodontidae, and more than 50% of all frogs are in just are fundamentally tied to water.
    [Show full text]
  • Porthidium Dunni (Hartweg and Oliver, 1938)
    Porthidium dunni (Hartweg and Oliver, 1938). Dunn’s Hognosed Pitviper is a “priority two species” that has been assessed Environmental Vulnerability Score of 16 (see the following article). This pitviper is found primarily at low elevations along the foothills of the Sierra Madre del Sur physiographic region and the coastal plain of the Planicie Costera del Pacífico and Planicie Costera de Tehuantepec physiographic regions (Mata-Silva et al., 2015b) in southern Oaxaca and extreme western Chiapas, Mexico. This individual was found ca. 3.6 km NNW of La Soledad, Municipio de Villa de Tututepec de Melchor Ocampo, Oaxaca. ' © Vicente Mata-Silva 543 www.mesoamericanherpetology.com www.eaglemountainpublishing.com The endemic herpetofauna of Mexico: organisms of global significance in severe peril JERRY D. JOHNSON1, LARRY DAVID WILSON2, VICENTE MATA-SILVA1, ELÍ GARCÍA-PADILLA3, AND DOMINIC L. DESANTIS1 1Department of Biological Sciences, The University of Texas at El Paso, El Paso, Texas 79968-0500, United States. E-mail: [email protected], and [email protected], and [email protected] 2Centro Zamorano de Biodiversidad, Escuela Agrícola Panamericana Zamorano, Departamento de Francisco Morazán, Honduras. E-mail: [email protected] 3Oaxaca de Juárez, Oaxaca 68023, Mexico. E-mail: [email protected] ABSTRACT: Life on Earth exists due to the interactions among the atmosphere, hydrosphere, and litho- sphere. Humans, however, have created and are faced with the consequences of an interrelated set of problems that impact all of these spheres, including the biosphere. The decline in the diversity of life is a problem of global dimensions resulting from a sixth mass extinction episode created by humans.
    [Show full text]
  • Northern Region MESOAMERICA BIODIVERSITY HOTSPOT
    Ecosystem Profile Northern Region Of The MESOAMERICA BIODIVERSITY HOTSPOT Belize, Guatemala, Mexico Final version January 15, 2004 TABLE OF CONTENTS INTRODUCTION ..........................................................................................................................1 THE ECOSYSTEM PROFILE.......................................................................................................1 BACKGROUND............................................................................................................................2 Biological Importance.............................................................................................................................. 2 Socioeconomic Context........................................................................................................................... 3 Progress in Conserving Biodiversity........................................................................................................ 4 CONSERVATION OUTCOMES ...................................................................................................5 Species Outcomes .................................................................................................................................. 6 Site Outcomes......................................................................................................................................... 7 Prioritization of the Key Biodiversity Areas.............................................................................................. 7 Corridor
    [Show full text]
  • Volume 2, Chapter 14-8: Salamander Mossy Habitats
    Glime, J. M. and Boelema, W. J. 2017. Salamander Mossy Habitats. Chapt. 14-8. In: Glime, J. M. Bryophyte Ecology. Volume 2. 14-8-1 Bryological Interaction.Ebook sponsored by Michigan Technological University and the International Association of Bryologists. Last updated 19 July 2020 and available at <http://digitalcommons.mtu.edu/bryophyte-ecology2/>. CHAPTER 14-8 SALAMANDER MOSSY HABITATS Janice M. Glime and William J. Boelema TABLE OF CONTENTS Tropical Mossy Habitats – Plethodontidae........................................................................................................ 14-8-3 Terrestrial and Arboreal Adaptations ......................................................................................................... 14-8-3 Bolitoglossa (Tropical Climbing Salamanders) ......................................................................................... 14-8-4 Bolitoglossa diaphora ................................................................................................................................ 14-8-5 Bolitoglossa diminuta (Quebrada Valverde Salamander) .......................................................................... 14-8-5 Bolitoglossa hartwegi (Hartweg's Mushroomtongue Salamander) ............................................................ 14-8-5 Bolitoglossa helmrichi ............................................................................................................................... 14-8-5 Bolitoglossa jugivagans ............................................................................................................................
    [Show full text]
  • Crotalus Tancitarensis. the Tancítaro Cross-Banded Mountain Rattlesnake
    Crotalus tancitarensis. The Tancítaro cross-banded mountain rattlesnake is a small species (maximum recorded total length = 434 mm) known only from the upper elevations (3,220–3,225 m) of Cerro Tancítaro, the highest mountain in Michoacán, Mexico, where it inhabits pine-fir forest (Alvarado and Campbell 2004; Alvarado et al. 2007). Cerro Tancítaro lies in the western portion of the Transverse Volcanic Axis, which extends across Mexico from Jalisco to central Veracruz near the 20°N latitude. Its entire range is located within Parque Nacional Pico de Tancítaro (Campbell 2007), an area under threat from manmade fires, logging, avocado culture, and cattle raising. This attractive rattlesnake was described in 2004 by the senior author and Jonathan A. Campbell, and placed in the Crotalus intermedius group of Mexican montane rattlesnakes by Bryson et al. (2011). We calculated its EVS as 19, which is near the upper end of the high vulnerability category (see text for explanation), its IUCN status has been reported as Data Deficient (Campbell 2007), and this species is not listed by SEMARNAT. More information on the natural history and distribution of this species is available, however, which affects its conservation status (especially its IUCN status; Alvarado-Díaz et al. 2007). We consider C. tancitarensis one of the pre-eminent flagship reptile species for the state of Michoacán, and for Mexico in general. Photo by Javier Alvarado-Díaz. Amphib. Reptile Conserv. | http://amphibian-reptile-conservation.org 128 September 2013 | Volume 7 | Number 1 | e71 Copyright: © 2013 Alvarado-Díaz et al. This is an open-access article distributed under the terms of the Creative Commons Attribution–NonCommercial–NoDerivs 3.0 Unported License, which permits unrestricted use for Amphibian & Reptile Conservation 7(1): 128–170.
    [Show full text]
  • Batrachochytrium Dendrobatidis And
    UNIVERSITY OF CALIFORNIA Los Angeles Assessing the threat of two deadly fungal pathogens (Batrachochytrium dendrobatidis and Batrachochytrium salamandrivorans) to amphibian biodiversity and the impacts of human- mediated movement of an invasive carrier species and climate change A dissertation submitted in partial satisfaction of the requirements for the degree of Doctor of Environmental Science and Engineering by Tiffany Ann Yap 2016 © Copyright by Tiffany Ann Yap 2016 Abstract of the Dissertation Assessing the threat of two deadly fungal pathogens (Batrachochytrium dendrobatidis and Batrachochytrium salamandrivorans) to amphibian biodiversity and the impacts of human- mediated movement of an invasive carrier species and climate change by Tiffany Ann Yap Doctor of Environmental Science and Engineering University of California, Los Angeles, 2016 Professor Richard F. Ambrose, Co-Chair Professor Vance T. Vredenburg, Co-Chair Batrachochytrium dendrobatidis (Bd), a fungal pathogen that causes chytridiomycosis in amphibians, has infected >500 species and caused declines and extinctions in >200 species. Recently, a second deadly fungal pathogen that also causes chytridiomycosis, Batrachochytrium salamandrivorans (Bsal) was discovered. The presence of these lethal pathogens in international trade threatens amphibian diversity. In this dissertation, I use a novel modeling approach to predict disease risk from Bd and/or Bsal to amphibian populations in North America and Asia by incorporating pathogen habitat suitability, host availability, the potential presence of an invasive carrier species, and pathogen invasion history. First I identify Bsal threat to North American salamanders to be greatest in the Southeast US, the West Coast, and highlands of Mexico. I then ii investigate the compounded risk of Bd and Bsal in North America and find highest relative risk in those same areas and in the Sierra Nevada Mountains and the northern Rocky Mountains.
    [Show full text]