Amphibia and Reptilia
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Diversification and Cryptic Diversity of Ophisops Elegans (Sauria, Lacertidae)
Received: 22 July 2019 | Revised: 10 December 2019 | Accepted: 20 December 2019 DOI: 10.1111/jzs.12369 ORIGINAL ARTICLE Diversification and cryptic diversity of Ophisops elegans (Sauria, Lacertidae) Claudine Montgelard1,2 | Roozbeh Behrooz1 | Véronique Arnal1 | Atefeh Asadi1 | Philippe Geniez1 | Mohammad Kaboli3 1CEFE, PSL-EPHE (Biogéographie et Ecologie des Vertébrés), CNRS, Université de Abstract Montpellier, Univ Paul Valéry Montpellier 3, Revealing cryptic diversity constitutes the backbone of the future identification and IRD, Montpellier, France description of a new lineage. For the genus Ophisops (Lacertidae), previous studies 2Department of Zoology, Centre for Ecological Genomics and Wildlife indicated that this genus is characterized by cryptic diversity as three clades were Conservation, University of Johannesburg, obtained for O. elegans and O. occidentalis that do not fit the classical systematics. Johannesburg, South Africa 3Department of Environmental Science, Notably, we were interested to delineate the distribution range of the two clades Faculty of Natural Resources, University of of O. elegans described in Iran. We sequenced 65 individuals of Ophisops mainly Tehran, Karaj, Iran from northwestern Iran for one mitochondrial (cytochrome c oxidase subunit 1 [COI]; Correspondence 686 base pairs [bp]) and three nuclear genes (R35, MC1R, and PKM2; 1,857 bp). Claudine Montgelard, Biogéographie et Ecologie des Vertébrés (EPHE), Centre Phylogeographic analysis from mitochondrial and nuclear genes confirmed that d'Ecologie Fonctionnelle et Evolutive (UMR Iranian samples belong to two major haplogroups (divergence of 13% for COI) that 5175 CNRS), 1919 route de Mende, 34293 Montpellier cedex 5, France. are also split into several subclades (divergence of 6%–10% for COI), revealing an Email: [email protected] unsuspected diversity within Iranian Ophisops. -
Accounting for Uncertainty in Assessing the Impact of Climate Change on Biodiversity Hotspots in Spain
Animal Biodiversity and Conservation 42.2 (2019) 355 Accounting for uncertainty in assessing the impact of climate change on biodiversity hotspots in Spain D. Romero, J. Olivero, R. Real Romero, D., Olivero, J., Real, R., 2019. Accounting for uncertainty in assessing the impact of climate change on biodiversity hotspots in Spain. Animal Biodiversity and Conservation, 42.2: 355–367, Doi: https://doi. org/10.32800/abc.2019.42.0355 Abstract Accounting for uncertainty in assessing the impact of climate change on biodiversity hotspots in Spain. Our limited understanding of the complexity of nature generates uncertainty in mathematical and cartographical models used to predict the effects of climate change on species’ distributions. We developed predictive models of distributional range shifts of threatened vertebrate species in mainland Spain, and in their accumulation in biodiversity hotspots due to climate change. We considered two relevant sources of climatological uncertainty that affect predictions of future climate: general circulation models and socio–economic scenarios. We also examined the relative im- portance of climate as a driver of species' distribution and taxonomic uncertainty as additional biogeographical causes of uncertainty. Uncertainty was detected in all the forecasts derived from models in which climate was a significant explanatory factor, and in the species with taxonomic uncertainty. Uncertainty in forecasts was mainly located in areas not occupied by the species, and increased with time difference from the present. Mapping this uncertainty allowed us to assess the consistency of predictions regarding future changes in the distribution of hotspots of threatened vertebrates in Spain. Key words: Climate change, Prediction accuracy, Taxonomic uncertainty, Threatened species, Uncertainty mapping Resumen Considerar la incertidumbre en la evaluación de los efectos del cambio climático en las zonas de gran diversidad de España. -
Ship Rats and Island Reptiles: Patterns of Co-Existence in the Mediterranean
Ship rats and island reptiles: patterns of co-existence in the Mediterranean Daniel Escoriza GRECO, University of Girona, Girona, Girona, Spain ABSTRACT Background. The western Mediterranean archipelagos have a rich endemic fauna, which includes five species of reptiles. Most of these archipelagos were colonized since early historic times by anthropochoric fauna, such as ship rats (Rattus rattus). Here, I evaluated the influence of ship rats on the occurrence of island reptiles, including non-endemic species. Methodology. I analysed a presence-absence database encompassing 159 islands (Balearic Islands, Provence Islands, Corso-Sardinian Islands, Tuscan Archipelago, and Galite) using Bayesian-regularized logistic regression. Results. The analysis indicated that ship rats do not influence the occurrence of endemic island reptiles, even on small islands. Moreover, Rattus rattus co-occurred positively with two species of non-endemic reptiles, including a nocturnal gecko, a guild considered particularly vulnerable to predation by rats. Overall, the analyses showed a very different pattern than that documented in other regions of the globe, possibly attributable to a long history of coexistence. Subjects Biodiversity, Biogeography, Conservation Biology, Ecology, Zoology Keywords Alien species, Co-occurrences, Extinction, Island endemic, Lizard INTRODUCTION The Mediterranean basin is a hotspot of biodiversity, but it is also one of the regions Submitted 19 November 2019 Accepted 28 February 2020 in which biodiversity is most threatened, specifically by the massive transformation of Published 19 March 2020 landscapes and the spread of alien species (Médail & Quézel, 1999). The loss of biodiversity Corresponding author in the region began in ancient times, shortly after human colonization of the islands (Vigne, Daniel Escoriza, 1992). -
B O C a G I a N a Museu Municipal Do Funchal (História Natural)
1 ISSN 0523 - 7904 B O C A G I A N A Museu Municipal do Funchal (História Natural) Madeira 30.VIII.2009 No. 223 TRABALHOS DE ZOÓLOGOS GERMÂNICOS SOBRE A MADEIRA (1916-2000) POR EBERHARD AXEL WILHELM 1 ABSTRACT. Written contributions made by German-speaking zoologists on Madeira (1916-2000). Between 1916 and 2000, a considerable number of German-speaking zoologists (Germans, Austrians, Swiss and also Luxemburgers) have visited Madeira and / or described animals from this island, having published their findings in several magazines and / or books. In the present list, data on those naturalists are presented. Additional data to the previous list (WILHELM, 1997) is also given in an addendum. It is clear that a certain number of naturalists have published their findings based on specimen collected by others, thus not having visited the island. 1 Rua Senhora da Conceição, 42-3D, 2695-854 Bobadela, Portugal. E-mails: [email protected] (part.); [email protected] (min. neg. estr.). 1 ISSN 0523 - 7904 B O C A G I A N A Museu Municipal do Funchal (História Natural) Madeira 30.VIII.2009 No. 223 TRABALHOS DE ZOÓLOGOS GERMÂNICOS SOBRE A MADEIRA (1916-2000) POR EBERHARD AXEL WILHELM 1 ABSTRACT. Written contributions made by German-speaking zoologists on Madeira (1916-2000). Between 1916 and 2000, a considerable number of German-speaking zoologists (Germans, Austrians, Swiss and also Luxemburgers) have visited Madeira and / or described animals from this island, having published their findings in several magazines and / or books. In the present list, data on those naturalists are presented. Additional data to the previous list (WILHELM, 1997) is also given in an addendum. -
Frogs and Toads of Rhode Island
FROG & TOAD Chug-o-rum! Peep-peeep-peeep! Kraack-arrack! Frogs and toads thrive in the many ponds, forests , felds and open woodlands found on Audubon wildlife refuges. Spring and summer are great times to look and listen for them. Listed below are the common species found in Rhode Island. Bullfrog Northern Leopard Frog (Rana catesbeiana) (Rana pipiens) Bullfrogs are the largest frog in the United States Leopard frogs, as their name implies, are covered and have smooth, dull green to brown skin with in many, round black spots with lighter outlines. dark spots. Males have a yellow chin, and females Teir base color is usually brown or green but can have a white chin. Males make a deep echoing vary into yellow or blue. Tey have raised, golden croak “Chug-o-rum, Chug-o-rum” call in early ridges running down their back. Tey can be found summer. It can sound like a cow mooing, which in meadows and grasslands in the warmer months is why the word “bull” is in its name. Tey eat and near ponds and streams during breeding season. many insects, but will also eat fsh, rodents and Teir calls sound like a mix of “chucks” and “old small birds. creaky door” sounds. Green Frog Pickerel Frog (Rana clamitans) (Rana palustris) Green frogs greatly resemble bullfrogs, with a bright Nearly the twin of the leopard frog, pickerel green head and shoulders and hints of brown, blue or frogs are distinguished by their spots being black, but can be distinguished by the raised ridges square shaped rather than round and a bright down their backs. -
The Case of the Missing Frogs by Bryan Hamilton Why Are There No
The Case of the Missing Frogs By Bryan Hamilton Why are there no frogs in Great Basin National Park? Great Basin National Park seems like a perfect refuge for frogs, with plenty of water--ten perennial streams, hundreds of springs, and six alpine lakes, but apparently there are no amphibians. During 2002, an amphibian inventory was conducted within Great Basin National Park. Crews surveyed perennial streams, springs, and alpine lakes, but did not observe any adult amphibians, tadpoles, or egg masses. The reasons for this are unclear, but apparently frog distribution depends on more than just abundant water. Lack of suitable breeding habitat is a major limiting factor in amphibian distribution. Most amphibians require still or extremely slow moving water to lay their eggs in. High gradient streams in the Park do not provide appropriate breeding habitat. The hundreds of springs in the Park may provide this habitat, however, no amphibians were found at the dozens of springs surveyed this year. Isolation from source populations is another limiting factor. Streams leave the Park and then quickly disappear underground. Amphibian populations near the Park are not directly connected to these streams. Thus no corridors exist between the Park and nearby amphibian populations. One amphibian species that does not require aquatic corridors for migration is the Great Basin Spadefoot (Spea intermontana), commonly referred to as a "toad." Spadefoots are distinguished from "true toads" (members of the family Bufonidae) by a black wedge shaped spade on their hind feet, used for burrowing. Spadefoots move considerable distances over land during spring and summer rains, travelling to breeding sites. -
Podarcis Pityusensis, Ibiza Wall Lizard
The IUCN Red List of Threatened Species™ ISSN 2307-8235 (online) IUCN 2008: T17800A7482971 Podarcis pityusensis, Ibiza Wall Lizard Assessment by: Valentin Pérez-Mellado, Iñigo Martínez-Solano View on www.iucnredlist.org Citation: Valentin Pérez-Mellado, Iñigo Martínez-Solano. 2009. Podarcis pityusensis. The IUCN Red List of Threatened Species 2009: e.T17800A7482971. http://dx.doi.org/10.2305/IUCN.UK.2009.RLTS.T17800A7482971.en Copyright: © 2015 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale, reposting or other commercial purposes is prohibited without prior written permission from the copyright holder. For further details see Terms of Use. The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. The IUCN Red List Partners are: BirdLife International; Botanic Gardens Conservation International; Conservation International; Microsoft; NatureServe; Royal Botanic Gardens, Kew; Sapienza University of Rome; Texas A&M University; Wildscreen; and Zoological Society of London. If you see any errors or have any questions or suggestions on what is shown in this document, please provide us with feedback so that we can correct or extend the information provided. THE IUCN -
Lista Patrón De Los Anfibios Y Reptiles De España (Actualizada a Diciembre De 2014)
See discussions, stats, and author profiles for this publication at: http://www.researchgate.net/publication/272447364 Lista patrón de los anfibios y reptiles de España (Actualizada a diciembre de 2014) TECHNICAL REPORT · DECEMBER 2014 CITATIONS READS 2 383 4 AUTHORS: Miguel A. Carretero Inigo Martinez-Solano University of Porto Estación Biológica de Doñana 256 PUBLICATIONS 1,764 CITATIONS 91 PUBLICATIONS 1,158 CITATIONS SEE PROFILE SEE PROFILE Enrique Ayllon Gustavo A. Llorente ASOCIACION HERPETOLOGICA ESPAÑOLA University of Barcelona 30 PUBLICATIONS 28 CITATIONS 210 PUBLICATIONS 1,239 CITATIONS SEE PROFILE SEE PROFILE Available from: Inigo Martinez-Solano Retrieved on: 13 November 2015 Lista patrón de los anfibios y reptiles de España | Diciembre 2014 Lista patrón de los anfibios y reptiles de España (Actualizada a diciembre de 2014) Editada por: Miguel A. Carretero Íñigo Martínez-Solano Enrique Ayllón Gustavo Llorente (Comisión permanente de taxonomía de la AHE) La siguiente lista patrón tiene como base la primera lista patrón: MONTORI, A.; LLORENTE, G. A.; ALONSO-ZARAZAGA, M. A.; ARRIBAS, O.; AYLLÓN, E.; BOSCH, J.; CARRANZA, S.; CARRETERO, M. A.; GALÁN, P.; GARCÍA-PARÍS, M.; HARRIS, D. J.; LLUCH, J.; MÁRQUEZ, R.; MATEO, J. A.; NAVARRO, P.; ORTIZ, M.; PÉREZ- MELLADO, V.; PLEGUEZUELOS, J. M.; ROCA, V.; SANTOS, X. & TEJEDO, M. (2005): Conclusiones de nomenclatura y taxonomía para las especies de anfibios y reptiles de España. MONTORI, A. & LLORENTE, G. A. (coord.). Asociación Herpetológica Española, Barcelona. En caso de aquellos ítems sin comentarios, la información correspondiente se encuentra en esta primera lista, que está descargable en: http://www.magrama.gob.es/es/biodiversidad/temas/inventarios- nacionales/lista_herpetofauna_2005_tcm7-22734.pdf Para aquellos ítems con nuevos comentarios, impliquen o no su modificación, se adjunta la correspondiente explicación con una clave numerada (#). -
Teira Dugesii (Sauria: Lacertidae) – High Aggregation
NATURAL HISTORY NOTE The Herpetological Bulletin 139, 2017: 31-32 Teira dugesii (Sauria: Lacertidae) – high aggregation DANIEL KOLESKA*, VLADIMIR VRABEC & MARTIN KULMA ¹Department of Zoology and Fisheries, Faculty of Agrobiology Food and Natural Resources, Czech University of Life Sciences, Prague, Kamýcká 129, 165 00, Praha, Czech Republic *Corresponding author Email: [email protected] he Madeiran wall lizard Teira dugesii (Milne-Edwards, (VV) noticed a very high aggregation of T. dugesii (>30, 1829) is endemic to the Madeiran archipelago (Kwet, males and females) on a single spot (Fig. 1). Many more T2009), where it occurs in a wide range of habitats from sea individuals (>100) were observed on cracked sun-exposed level up to mountain tops (Sadek, 1981). However, several rocks in the surroundings. A steep rocky slope represented populations (probably introduced by human activity) have the general site with numerous loopholes providing been also reported from the city of Lisbon, Portugal (Sá- potential shelters. Weather conditions at the time were Sousa, 1995), Selvagens islands (Bischoff et al., 1989) and rather cloudy with occasional sunshine and temperature several islands of the Azore archipelago (Malkmus, 1984). between 15 - 18 °C. The aggregation possibly involved T. dugesii is omnivorous with a diet consisting mainly of thermoregulation as the location was in a sunny locality insects, plant leaves, flowers, pollens, fruits and seeds. and that also provided many potential retreat sites. Plant residues (nectar, blooms, leaves) may even represent Aggregation behaviour is known in many lizard species; up to 60 % of the diet (Sadek, 1981). This species is also e.g. large numbers of marine iguanas Amblyrhynchus considered to be the first lizard reported to consume plant cristatus on small areas of Galapagos reefs (Eibl- nectar (Elvers, 1977) and occasional predation on seabird’s Eibesfeldt, 1984). -
Psonis Et Al. 2017
Molecular Phylogenetics and Evolution 106 (2017) 6–17 Contents lists available at ScienceDirect Molecular Phylogenetics and Evolution journal homepage: www.elsevier.com/locate/ympev Hidden diversity in the Podarcis tauricus (Sauria, Lacertidae) species subgroup in the light of multilocus phylogeny and species delimitation ⇑ Nikolaos Psonis a,b, , Aglaia Antoniou c, Oleg Kukushkin d, Daniel Jablonski e, Boyan Petrov f, Jelka Crnobrnja-Isailovic´ g,h, Konstantinos Sotiropoulos i, Iulian Gherghel j,k, Petros Lymberakis a, Nikos Poulakakis a,b a Natural History Museum of Crete, School of Sciences and Engineering, University of Crete, Knosos Avenue, Irakleio 71409, Greece b Department of Biology, School of Sciences and Engineering, University of Crete, Vassilika Vouton, Irakleio 70013, Greece c Institute of Marine Biology, Biotechnology and Aquaculture, Hellenic Center for Marine Research, Gournes Pediados, Irakleio 71003, Greece d Department of Biodiversity Studies and Ecological Monitoring, T.I. Vyazemski Karadagh Scientific Station – Nature Reserve of RAS, Nauki Srt., 24, stm. Kurortnoe, Theodosia 298188, Republic of the Crimea, Russian Federation e Department of Zoology, Comenius University in Bratislava, Mlynská dolina, Ilkovicˇova 6, 842 15 Bratislava, Slovakia f National Museum of Natural History, Sofia 1000, Bulgaria g Department of Biology and Ecology, Faculty of Sciences and Mathematics, University of Niš, Višegradska 33, Niš 18000, Serbia h Department of Evolutionary Biology, Institute for Biological Research ‘‘Siniša Stankovic´”, -
Threatened Species List Spain
THREATENED SPECIES LIST SPAIN Threatened species included in the national inventory of the Ministry of MARM and/or in the Red List of the International Union for Conservation of Nature (IUCN) that are or may be inhabited in the areas of our Hydro Power Stations. 6 CRITIC ENDANGERED SPECIES (CR) GROUP SPECIE COMMON NAME CATEGORY (MARM) (IUCN) Birds Neophron percnopterus Egyptian Vulture CR EN Botaurus stellaris Great Bittern CR LC Mammals Lynx pardinus Iberian Lynx CR CR Ursus arctos Brown Bear CR (Northern Spain) LC Invertebrates Belgrandiella galaica Gastropoda CR No listed Macromia splendens Splendid Cruiser CR VU 24 ENDANGERED SPECIES (EN) GROUP SPECIE COMMON NAME CATEGORY (MARM) (IUCN) Amphibians Rana dalmatina Agile Frog EN LC Birds Pyrrhocorax pyrrhocorax Chough EN LC Hieraaetus fasciatus Bonelli´s Eagle EN LC Alectoris rufa Barbary Partridge EN LC Parus caeruleus Blue Tit EN LC Tyto alba Barn Owl EN LC Burhinus oedicnemus Stone Curlew EN LC Corvus corax Common Raven EN LC Chersophilus duponti Dupont´s Lark EN NT Milvus milvus Red Kite EN NT Aquila adalberti Spanish Imperial Eagle EN VU Cercotrichas galactotes Alzacola EN LC Reptiles Algyroides marchi Spanish Algyroides EN EN Emys orbicularis European Pond Turtle EN NT Mammals Rhinolophus mehelyi Mehely´s Horseshoe Bat EN VU Mustela lutreola European Mink EN EN Myotis capaccinii Long –Fingered bat EN VU Freshwater fish Salaria fluviatilis Freshwater blenny EN LC Chondrostoma turiense Madrija (Endemic) EN EN Cobitis vettonica Colmilleja del Alagón EN EN (Endemic) Invertebrates Gomphus -
<I>Salamandra Salamandra</I>
International Journal of Speleology 46 (3) 321-329 Tampa, FL (USA) September 2017 Available online at scholarcommons.usf.edu/ijs International Journal of Speleology Off icial Journal of Union Internationale de Spéléologie Subterranean systems provide a suitable overwintering habitat for Salamandra salamandra Monika Balogová1*, Dušan Jelić2, Michaela Kyselová1, and Marcel Uhrin1,3 1Institute of Biology and Ecology, Faculty of Science, P. J. Šafárik University, Šrobárova 2, 041 54 Košice, Slovakia 2Croatian Institute for Biodiversity, Lipovac I., br. 7, 10000 Zagreb, Croatia 3Department of Forest Protection and Wildlife Management, Faculty of Forestry and Wood Sciences, Czech University of Life Sciences, Kamýcká 1176, 165 21 Praha, Czech Republic Abstract: The fire salamander (Salamandra salamandra) has been repeatedly noted to occur in natural and artificial subterranean systems. Despite the obvious connection of this species with underground shelters, their level of dependence and importance to the species is still not fully understood. In this study, we carried out long-term monitoring based on the capture-mark- recapture method in two wintering populations aggregated in extensive underground habitats. Using the POPAN model we found the population size in a natural shelter to be more than twice that of an artificial underground shelter. Survival and recapture probabilities calculated using the Cormack-Jolly-Seber model were very constant over time, with higher survival values in males than in females and juveniles, though in terms of recapture probability, the opposite situation was recorded. In addition, survival probability obtained from Cormack-Jolly-Seber model was higher than survival from POPAN model. The observed bigger population size and the lower recapture rate in the natural cave was probably a reflection of habitat complexity.