Curriculum Vitae – Dr Crisanto Gómez 1

Total Page:16

File Type:pdf, Size:1020Kb

Curriculum Vitae – Dr Crisanto Gómez 1 Curriculum vitae – Dr Crisanto Gómez Curriculum vitae Dr. Crisanto Gómez López Marzo de 2014 1 Curriculum vitae – Dr Crisanto Gómez Datos personales: Apellidos y nombre: GÓMEZ LÓPEZ, CRISANTO Categoría actual como Docente: Catedrático de Universidad Departamento o Unidad Docente actual: Departamento de Ciencias Ambientales Unidad de Biología Animal Facultad o Escuela actual: Facultad de Ciencias. Universidad de Girona. Títulos Académicos .Licenciado en Ciencias Biológicas por la Universidad Autónoma de Barcelona. Fecha de expedición del título: 18-07-1991. .Doctor en Ciencias Biológicas por la Universidad Autónoma de Barcelona. Fecha de expedición del título: 29-02-1996. Calificación: Apto Cum Laude. Actividad Investigadora 1. Difusión de resultados de la Actividad Investigadora Publicaciones Científicas en Revistas Indexadas 1. Espadaler X & Gómez C. 1996. Seed production, predation and dispersal in the Mediterranean myrmecochore Euphorbia characias (Euphorbiaceae). Ecography, 19: 7-15. 2. Espadaler X. & Gómez C. 1997. Soil surface searching and transport of Euphorbia characias seeds by ants. Acta Oecologica, 18(1): 39-46. 2 Curriculum vitae – Dr Crisanto Gómez 3. Gómez C & Espadaler X. 1997. Falling or movement of seeds and the presence of an elaiosome: its effect on ant reaction in a myrmecochorous species, Euphorbia characias (Euphorbiaceae). Sociobiology 30(2): 175-183. 4. Gómez C & Espadaler X. 1997. Myrmecochorous dispersal distance: a world survey. Journal of Biogeography. 25: 573-580. 5. Gómez C & Espadaler X. 1998. Aphaenogaster senilis Mayr (Hymenoptera, Formicidae): a possible parasite in the myrmecochory of Euphorbia characias. Sociobiology 32: 441-450. 6. Gómez C & Espadaler X. 1998. The seed dispersal curve of a Mediterranean myrmecochore: influence of ant size and the distance to nest. Ecological Research 13: 347-354. 7. Espadaler X & Gómez C. 2000. Formica dusmeti Emery, 1909, an Iberian endemic ant species: description of the male and distribution (Hymenoptera, Formicidae). Annales Zoologici 50: 39-41. 8. Gómez C & Espadaler X. 2000. Species body-size distribution and spatial scale in Iberian ants. Vie et Milieu 50: 289-295. 9. Espadaler X & Gómez C. 2001. Formicine ants do comply with the size-grain hypothesys. Functional Ecology 15: 136-139. 10. Espadaler X & Gómez C. 2001. Female performance in Euphorbia characias: effect of flower position on seed quantity and quality. Seed Science Research 11: 163-172. 11. Espadaler X & Gómez C. 2002. The species body-size distribution in iberian ants is parameter independent. Vie et Milieu 52 (2/3): 103-107. 12. Espadaler X & Gómez C. 2003. The Argentine Ant, Linepithema humile, in the Iberian Peninsula. Sociobiology 42: 187-192. 13. Gómez C, Casellas D, Oliveras J & Bas JM. 2003. Structure of ground-foraging ant assemblages and land-use change in rural ecosystems in the north-western mediterranean region. Biodiversity and Conservation 12:2135-2146. 14. Gómez C, Pons P & Bas JM. 2003. Effects of the Argentine ant (Linepithema humile Mayr) on seed dispersal and seedling emergence of Rhamnus alaternus L. (Rhamnaceae). Ecography 26: 532- 538. 3 Curriculum vitae – Dr Crisanto Gómez 15. Gómez, C. & Oliveras, J. 2003. Can the Argentine ant (Linepithema humile Mayr) replace native ants in myrmecochory? Acta Oecologica 24: 47-53. 16. Roura-Pascual N, Suarez AV, Gómez C, Pons P, Touyama Y, Wild AL & Towsend Peterson A. 2004. Geographic potential of Argentine ants (Linepithema humile Mayr) in the face of global climate change. Proceedings of the Royal Society of London Serie B. 271 (1557): 2527-2535. 17. Bas JM, Pons P & Gómez C. 2005. Home range and territory of Sardinian Warbler Sylvia melanocephala in a Mediterranean shrubland. Bird Study 52:137-144. 18. Bas JM, Gómez C, & Pons P. 2005. Fruit production and predispersal seed fall and predation of Rhamnus alaternus (Rhamnaceae). Acta Oecologica 27/2: 115-123. 19. Oliveras J, Bas JM, Casellas D & Gómez C. 2005. Numerical dominance of the Argentine ant vs native ants and consequences on soil resource searching in Mediterranean Cork-oak forest (Hymenoptera: Formicidae). Sociobiology 45: 643-658. 20. Oliveras J, Bas JM & Gómez C. 2005. Reduction of the ant mandible gap range after biotic homogeneization caused by an ant invasion (Hymenoptera: Formicidae). Sociobiology 45: 829-838. 21. Blancafort X & Gómez C. 2005. Consequences of the Argentine ant, Linepithema humile (Mayr), invasion on pollination of Euphorbia characias (L.) (Euphorbiaceae). Acta Oecologica 28/1: 49-55. 22. Oliveras J, Bas JM, Gómez C. 2005. Long-term consequences of the alteration of the seed dispersal process of Euphorbia characias L. due to the Argentine ant invasion. Ecography 28: 662- 672. 23. Gómez C, Espadaler X & Bas JM. 2005. Ant behaviour and seed morphology: a missing link of myrmecochory. Oecologia 146 (2): 244-246. 24. Bas JM, Pons P & Gómez C. 2006. Exclusive frugivory and seed dispersal of Rhamnus alaternus in the bird breeding season. Plant Ecology 183/01: 77-89. 25. Blancafort X & Gómez C. 2006. Downfall of pollen carriage by ants after Argentine ant invasion in two Mediterranean Euphorbia species. Vie et Milieu-Life and Environment 56 : 243-246. 4 Curriculum vitae – Dr Crisanto Gómez 26. Núria Roura-Pascual, Andrew V. Suarez, Crisanto Gómez, Pere Pons, Yoshifumi Touyama, Alexander L. Wild, Kristina McNyset, Ferran Gascon & A. Townsend Peterson. 2006. Niche Differentiation and Fine-scale Projections for Argentine Ants based on Remotely-sensed Data. Ecological Applications 16: 1832-1841. 27. Oliveras J, Bas JM & Gómez C. 2007. A shift in seed harvesting by ants following argentine ant invasion. Vie et Milieu 57(1/2) : 75-82. 28. Bas JM, Oliveras J & Gómez C. 2007. Final seed fate and seedling emergence in myrmecochorous plants: effects of ants and plant species. Sociobiology. 50 (1): 101-111. 29. Abril S, Oliveras J & Gómez C. 2007. Foraging activity and dietary spectrum of the Argentine ant (Linepithema humile Mayr) in invaded natural areas of the NE Iberian Peninsula. Environmental Entomology 36(5): 1166-1173. 30. Bas JM, Pons P, Gómez C. 2007. Daily activity of the sardinian warbler (Sylvia melanocephala) in the breeding season. Ardeola 54 : 335-338 31. Abril S, Oliveras J & Gómez C. 2008. Effect of temperature on the oviposition rate of Argentine ant queens (Linepithema humile Mayr) under monogynous and polygynous experimental conditions. Journal of Insect Physiology 54: 265-272. 32. Abril S, Oliveras J & Gómez C. 2008. Effect of seasonal dynamics on queen densities of the Argentine ant (Linepithema humile) (Hymenoptera:Formicidae) in an invaded natural area of the NE Iberian Peninsula. Sociobiology 51:645-654. 33. Oliveras J, Bas JM, Gómez C, Espadaler X. 2008. Mechanical defense in seeds to avoid predation by a granivorous ant. Naturwissenschaften 95: 501-506. 34. Abril S, Oliveras J & Gómez C. 2009. Effect of temperature on the Argentine ant’s development and survival. Journal of Insect Science. 10:97 35. Abril S & Gómez C. 2009. Ascertaining key factors behind the coexistence of the native ant species Plagiolepis pygmaea with the invasive argentine ant Linepithema humile (Hymenoptera :Formicidae). Sociobiology 53 : 559-568. 36. Bas, J.M.; Oliveras, J.; Gómez, C. 2009. Myrmecochory and short-term seed fate in Rhamnus alaternus: ant species and seed characteristics. Acta Oecologica 35:380-384. 5 Curriculum vitae – Dr Crisanto Gómez 37. Abril S, Roura-Pascual N, Oliveras J & Gómez C. 2009. Assesing the distribution of the Argentine ant using physiological data. Acta Oecologica 35: 739-745 38. Casellas D, Gómez C & Clavero M. 2009. Comparing methods of evaluating the spread of the Argentine ant in natural habitats: pitfall traps vs. baiting. Sociobiology 53:927-938. 39. Abril S & Gómez C. 2011. Aggressive behaviour of the two European Argentine ant supercolonies (Hymenoptera: Formicidae) towards displaced native ant species of the northeastern Iberian Peninsula. Myrmecological News 14: 99-106. 40. Núria Roura-Pascual, Cang Hui, Takayoshi Ikeda, Gwénaël Leday, David M Richardson, Soledad Carpintero, Xavier Espadaler, Crisanto Gómez, Benoit Guénard, Stephen Hartley, Paul Krushelnycky, Philip J. Lester, Melodie A McGeoch, Sean B. Menke, Jes S. Pedersen, Joel Pitt, Joaquin Reyes, Nathan J. Sanders, Andrew V. Suarez, Yoshifumi Touyama, Darren Ward, Philip S. Ward, Sue P. Corner. 2011. The relative role of climatic suitability and anthropogenic influence in determining the pattern of spread in a global invader. Proceedings of the Nacional Academy of Sciences USA. 108:220-225. 41. Gómez, C & Abril, S. 2011. Selective logging in public forest of central Iberian peninsula: effects of the recovery process on ant assemblages. Forest Ecology & Management. 262:1061-1066. 42. Gómez, C & Abril, S. 2012. Nuptial flights of the seed-harvester ant Messor barbarus (LINNAEUS, 1767) (Hymenoptera: Formicidae) in the Iberian Peninsula: synchrony, spatial scale and weather conditions. Myrmecological News. 16:25-29. 43. Boieiro M, Espadaler X, Gómez C & Eustaquio A. 2012. Spatial variation in the fatty acid composition of elaiosomes in an ant-dispersed plant: Differences within and between indviduals and populations. FLORA 207:497-502. 44. Abril S, Díaz M, Enríquez ML & Gómez C. 2013. More and bigger queens: a clue to the invasive success of the Argentine ant (Hymenoptera: Formicidae) in natural habitats. Myrmecological News 18:19-24. 45. Díaz M, Abril S, Enríquez M.L. & Gómez C. 2013. Where to move in winter: attractive areas for winter nesting in the Argentine ant. Myrmecological News 18:51-58. 6 Curriculum vitae – Dr Crisanto Gómez 46. Abril S & Gómez C. 2013. Rapid assessment of the ant assemblages in public pine forests of the central Iberian Peninsula. Forest Ecology & Management 293:79-84. 47. Gómez, C & Espadaler X. 2013. An update the world survey of myrmecochorous dispersal distances. Ecography 36:1193-1201. 48. Díaz M, Abril S, Enríquez M.L. & Gómez C. 2013. Assessment of the Argentine ant invasion management by means of manual removal of winter nests in mixed cork oak and pine forests. Biological Invasions doi: 10.1007/s10530-013-0520-1. 49. Miravete V, Roura-Pascual N, Dunn R & Gómez C.
Recommended publications
  • A Small Number of Workers with Specific Personality Traits Perform Tool Use in Ants Istva´ N Maa´ K1,2, Garyk Roelandt3, Patrizia D’Ettorre3,4*
    RESEARCH ARTICLE A small number of workers with specific personality traits perform tool use in ants Istva´ n Maa´ k1,2, Garyk Roelandt3, Patrizia d’Ettorre3,4* 1Department of Ecology, University of Szeged, Szeged, Hungary; 2Museum and Institute of Zoology, Polish Academy of Science, Warsaw, Poland; 3Laboratory of Experimental and Comparative Ethology UR 4443, University Sorbonne Paris Nord, Villetaneuse, France; 4Institut Universitaire de France (IUF), Paris, France Abstract Ants use debris as tools to collect and transport liquid food to the nest. Previous studies showed that this behaviour is flexible whereby ants learn to use artificial material that is novel to them and select tools with optimal soaking properties. However, the process of tool use has not been studied at the individual level. We investigated whether workers specialise in tool use and whether there is a link between individual personality traits and tool use in the ant Aphaenogaster senilis. Only a small number of workers performed tool use and they did it repeatedly, although they also collected solid food. Personality predicted the probability to perform tool use: ants that showed higher exploratory activity and were more attracted to a prey in the personality tests became the new tool users when previous tool users were removed from the group. This suggests that, instead of extreme task specialisation, variation in personality traits within the colony may improve division of labour. Introduction Tool use is a widespread phenomenon within the animal kingdom (Shumaker et al., 2011; Sanz et al., 2013) and new examples of animal tool use are regularly discovered, such as recently in *For correspondence: [email protected] pigs (Root-Bernstein et al., 2019) and seabirds (Fayet et al., 2020).
    [Show full text]
  • Setting Conservation Priorities for the Moroccan Herpetofauna: the Utility of Regional Red Listing
    Oryx—The International Journal of Conservation Setting conservation priorities for the Moroccan herpetofauna: the utility of regional red listing J uan M. Pleguezuelos,JosE´ C. Brito,Soum´I A F ahd,Mo´ nica F eriche J osE´ A. Mateo,Gregorio M oreno-Rueda,Ricardo R eques and X avier S antos Appendix 1 Nomenclatural and taxonomical combinations scovazzi (Zangari et al., 2006) for amphibians. Chalcides for the Moroccan (Western Sahara included) amphibians lanzai (Caputo & Mellado, 1992), Leptotyphlops algeriensis and reptiles for which there are potential problems re- (Hahn & Wallach, 1998), Macroprotodon brevis (Carranza garding taxonomic combinations; species names are fol- et al., 2004) and Telescopus guidimakaensis (Bo¨hme et al., lowed by reference to publications that support these 1989) for reptiles are considered here as full species. Macro- combinations. The complete list of species is in Appendix 2. protodon abubakeri has been recently described for the Agama impalearis (Joger, 1991), Tarentola chazaliae region (Carranza et al., 2004) and Hemidactylus angulatus (Carranza et al., 2002), Chalcides boulengeri, Chalcides recently found within the limits of the study area (Carranza delislei, Chalcides sphenopsiformis (Carranza et al., 2008), & Arnold, 2006). Filtering was not applied to species of Timon tangitanus, Atlantolacerta andreanszkyi, Podarcis passive introduction into Morocco, such as Hemidactylus vaucheri, Scelarcis perspicillata (Arnold et al., 2007), turcicus and Hemidactylus angulatus. The three-toed skink Hyalosaurus koellikeri
    [Show full text]
  • Short Term Response of Ants to the Removal of Ground Cover in Organic Olive Orchards
    Eur. J. Entomol. 108: 417–423, 2011 http://www.eje.cz/scripts/viewabstract.php?abstract=1632 ISSN 1210-5759 (print), 1802-8829 (online) Short term response of ants to the removal of ground cover in organic olive orchards MERCEDES CAMPOS1, LUISA FERNÁNDEZ1, FRANCISCA RUANO3, BELÉN COTES1, MANUEL CÁRDENAS1 and JUAN CASTRO2 1Department of Environmental Protection, Estación Experimental del Zaidín, (CSIC) C/Profesor Albareda n° 1, 18008 – Granada, Spain; e-mail: [email protected] 2IFAPA Centro Camino de Purchil, CAP (Junta de Andalucia), P.O. Box 2027, 18080 – Granada, Spain 3Department of Animal Biology, University of Granada, 18071 – Granada, Spain Key words. Hymenoptera, Formicidae, disturbance, biodiversity, soil management Abstract. Ants are the most abundant group of soil arthropods in olive groves where they are involved in various trophic relation- ships of great importance for crops. The system of soil management is one agricultural practice that has a great effect on ants, so the objective of this study was to compare ant populations in organic olive orchards with a ground cover of natural vegetation and others where this natural vegetation is mechanically removed at the beginning of June. Ants were sampled using pitfall traps at 14, 30, 70 and 90 days after the removal of the ground vegetation. Overall, ant biodiversity did not change. However, changes were observed in the abundance of ant species, in particular, in those species that build shallow nests in the soil, both between the rows of trees and under the canopy of olive trees. In contrast, deep nesting species, such as Messor barbarus, were not affected.
    [Show full text]
  • Reproductive Conflict Between Laying Workers in the Ant Aphaenogaster
    J Ethol DOI 10.1007/s10164-008-0145-5 ARTICLE Reproductive conflict between laying workers in the ant Aphaenogaster senilis Katsuya Ichinose Æ Alain Lenoir Received: 13 May 2008 / Accepted: 17 December 2008 Ó Japan Ethological Society and Springer 2009 Abstract Since workers of the ant Aphaenogaster senilis Keywords Aggression Á Ant Á Cuticular hydrocarbons Á can lay male eggs, reproductive conflict may occur Dominance Á Worker reproduction between these workers. We examined the occurrence of worker conflicts in groups of workers either with or without the queen. Intranidal aggression was observed in each nest Introduction for 10 min each day, and the immatures produced were counted once a week for two months. Pairs of workers Members of colonies of social insects benefit from involved in aggression were taken regularly from each nest cooperation (Ho¨lldobler and Wilson 1990). However, and used for chemical, morphological and anatomical apparently peaceful colonies may hide reproductive con- analyses. The attacker and the attacked workers differed in flicts of interest (Boomsma and Franks 2006; Ratnieks their cuticular hydrocarbon profiles. The attacker and the et al. 2006). Such hidden conflicts may occur, for example, attacked ants were at the same middle-aged fertile stage. when the workers are able to lay haploid eggs by arrhe- The attacker ant was significantly larger and more fertile notokous parthenogenesis, which may reduce colony than the attacked ant, and more mature physiologically fitness. In this situation, workers can try to monopolise (poison gland was darker). There was apparently no stable reproduction by dominance behaviour or they can destroy hierarchy between laying workers.
    [Show full text]
  • The Functions and Evolution of Social Fluid Exchange in Ant Colonies (Hymenoptera: Formicidae) Marie-Pierre Meurville & Adria C
    ISSN 1997-3500 Myrmecological News myrmecologicalnews.org Myrmecol. News 31: 1-30 doi: 10.25849/myrmecol.news_031:001 13 January 2021 Review Article Trophallaxis: the functions and evolution of social fluid exchange in ant colonies (Hymenoptera: Formicidae) Marie-Pierre Meurville & Adria C. LeBoeuf Abstract Trophallaxis is a complex social fluid exchange emblematic of social insects and of ants in particular. Trophallaxis behaviors are present in approximately half of all ant genera, distributed over 11 subfamilies. Across biological life, intra- and inter-species exchanged fluids tend to occur in only the most fitness-relevant behavioral contexts, typically transmitting endogenously produced molecules adapted to exert influence on the receiver’s physiology or behavior. Despite this, many aspects of trophallaxis remain poorly understood, such as the prevalence of the different forms of trophallaxis, the components transmitted, their roles in colony physiology and how these behaviors have evolved. With this review, we define the forms of trophallaxis observed in ants and bring together current knowledge on the mechanics of trophallaxis, the contents of the fluids transmitted, the contexts in which trophallaxis occurs and the roles these behaviors play in colony life. We identify six contexts where trophallaxis occurs: nourishment, short- and long-term decision making, immune defense, social maintenance, aggression, and inoculation and maintenance of the gut microbiota. Though many ideas have been put forth on the evolution of trophallaxis, our analyses support the idea that stomodeal trophallaxis has become a fixed aspect of colony life primarily in species that drink liquid food and, further, that the adoption of this behavior was key for some lineages in establishing ecological dominance.
    [Show full text]
  • Aphaenogaster Senilis
    Effect of social factors on caste differentiation in the ant Aphaenogaster senilis Camille Ruel ! EFFECT OF SOCIAL FACTORS ON CASTE DIFFERENTIATION IN THE ANT APHAENOGASTER SENILIS Camille RUEL A thesis submitted for the degree of Ph.D., Doctor of philosophy in biological science, at the Universitat Autònoma de Barcelona, Doctorado de Ecología Terrestre del CREAF (Centre de Recerca Ecològica i Aplicacions Forestals) Supervised by Xim Cerdá, Associate Professor of Research at the CSIC Raphaël Boulay, Professor at the Université de Tours Javier Retana, Professor at the Universitat Autònoma de Barcelona at the Estación Biológica de Doñana, Consejo Superior de Investigaciones Científicas, Sevilla, España and financed by JAE-doc grants, CSIC Xim Cerdá Raphaël Boulay Javier Retana Advisor Advisor Supervisor Camille Ruel January 2013 ! "! 2 À ma mère, à mon père, et à notre histoire. 3 Acknowledgments Aux hasards de la vie. À celui même qui m’a porté jusqu’à Séville, aux évènements qui m’ont décidés à m’engager dans cette longue aventure, et aux hasards des rencontres, qui enrichissent tant. À la tolérance, la curiosité, l’enrichissement, la découverte, la ténacité, la critique, la force. Quiero agradecer a mis 2 jefes, Xim y Raphaël, por darme esa oportunidad de trabajar con Aphaenogaster senilis en condiciones tan buenas. Gracias por su disponibilidad, gracias por estos 4 años. Une pensée pour Alain Lenoir et Abraham Hefetz. Merci pour votre soutien et vos enseignements. Por su ayuda a lo largo del doctorado : T. Monnin, A. Rodrigo, X. Espadaler y F. Garcia del Pino. Une petite pensée également pour le groupe de Jussieu, qui m’a donné le goût de la recherche et fait découvrir le monde passionnant des insectes sociaux.
    [Show full text]
  • Is Phenotypic Plasticity a Key Mechanism for Responding to Thermal Stress in Ants?
    Sci Nat (2017) 104:42 DOI 10.1007/s00114-017-1464-6 ORIGINAL PAPER Is phenotypic plasticity a key mechanism for responding to thermal stress in ants? Cristela Sánchez Oms1,2 & Xim Cerdá1 & Raphaël Boulay2 Received: 24 February 2017 /Revised: 12 April 2017 /Accepted: 21 April 2017 # Springer-Verlag Berlin Heidelberg 2017 Abstract Unlike natural selection, phenotypic plasticity al- Keywords Phenotypic plasticity . Ants . Aphaenogaster lows organisms to respond quickly to changing environmental senilis . Rearing temperature . Thermal resistance . Body size conditions. However, plasticity may not always be adaptive. In insects, body size and other morphological measurements have been shown to decrease as temperature increases. This Introduction relationship may lead to a physiological conflict in ants, where larger body size and longer legs often confer better thermal Predicting species’ responses to global warming is one of the resistance. Here, we tested the effect of developmental tem- major challenges in ecology and evolutionary biology. Under perature (20, 24, 28 or 32 °C) on adult thermal resistance in climate change, species are expected to either modify their the thermophilic ant species Aphaenogaster senilis.Wefound distributions (Parmesan et al. 1999), acclimate (Somero that no larval development occurred at 20 °C. However, at 2010) or adapt to new environmental conditions through nat- higher temperatures, developmental speed increased as ex- ural selection (Hoffmann and Sgrò 2011). If species cannot pected and smaller adults were produced. In thermal resistance adopt one of these solutions, they are likely to rapidly go tests, we found that ants reared at 28 and 32 °C had half-lethal extinct. There are numerous examples in the literature of nat- temperatures that were 2 °C higher than those of ants reared at ural populations responding to global warming with pheno- 24 °C.
    [Show full text]
  • Actes Des Colloques Insectes Sociaux
    U 2 I 0 E 0 I 2 S ACTES DES COLLOQUES INSECTES SOCIAUX Edité par l'Union Internationale pour l’Etude des Insectes Sociaux - Section française (sous la direction de François-Xavier DECHAUME MONCHARMONT et Minh-Hà PHAM-DELEGUE) VOL. 15 (2002) – COMPTE RENDU DU COLLOQUE ANNUEL 50e anniversaire - Versailles - 16-18 septembre 2002 ACTES DES COLLOQUES INSECTES SOCIAUX Edité par l'Union Internationale pour l’Etude des Insectes Sociaux - Section française (sous la direction de François-Xavier DECHAUME MONCHARMONT et Minh-Hà PHAM-DELEGUE) VOL. 15 (2002) – COMPTE RENDU DU COLLOQUE ANNUEL 50e anniversaire - Versailles - 16-18 septembre 2002 ISSN n° 0265-0076 ISBN n° 2-905272-14-7 Composé au Laboratoire de Neurobiologie Comparée des Invertébrés (INRA, Bures-sur-Yvette) Publié on-line sur le site des Insectes Sociaux : : http://www.univ-tours.fr/desco/UIEIS/UIEIS.htm Comité Scientifique : Martin GIURFA Université Toulouse Alain LENOIR Université Tours Christian PEETERS CNRS Paris 6 Minh-Hà PHAM-DELEGUE INRA Bures Comité d'Organisation : Evelyne GENECQUE F.X. DECHAUME MONCHARMONT Et toute l’équipe du LNCI (INRA Bures) Nous remercions sincèrement l’INRA et l’établissement THOMAS qui ont soutenu financièrement cette manifestation. Crédits Photographiques Couverture : 1. Abeille : Serge CARRE (INRA) 2. Fourmis : Photothèque CNRS 3. Termite : Alain ROBERT (Université de Bourgogne, Dijon) UIEIS Versailles Page 1 Programme UNION INTERNATIONALE POUR L’ETUDE DES INSECTES SOCIAUX UIEIS Section Française - 50ème Anniversaire Versailles 16-18 Septembre 2002 PROGRAMME Lundi 16 septembre 9 h ACCUEIL DES PARTICIPANTS - CAFE 10 h Présentation du Centre INRA de Versailles – Président du Centre Session Plasticité et Socialité- Modérateur Martin Giurfa 10 h 15 - Conférence Watching the bee brain when it learns – Randolf Menzel (Université Libre de Berlin) 11 h 15 Calcium responses to queen pheromones, social pheromones and plant odours in the antennal lobe of the honey bee drone Apis mellifera L.
    [Show full text]
  • Trees Increase Ant Species Richness and Change Community Composition in Iberian Oak Savannahs
    diversity Article Trees Increase Ant Species Richness and Change Community Composition in Iberian Oak Savannahs Álvaro Gaytán 1,* , José L. Bautista 2, Raúl Bonal 2,3 , Gerardo Moreno 2 and Guillermo González-Bornay 2 1 Department of Ecology, Environment and Plant Sciences, Stockholm University, 114-18 Stockholm, Sweden 2 Grupo de investigación Forestal, INDEHESA, University of Extremadura, 10600 Plasencia, Spain; [email protected] (J.L.B.); [email protected] (R.B.); [email protected] (G.M.); [email protected] (G.G.-B.) 3 Department of Biodiversity, Ecology and Evolution, Complutense University of Madrid, 28040 Madrid, Spain * Correspondence: [email protected] Abstract: Iberian man-made oak savannahs (so called dehesas) are traditional silvopastoral systems with a high natural value. Scattered trees provide shelter and additional food to livestock (cattle in our study sites), which also makes possible for animals depending on trees in a grass-dominated landscape to be present. We compared dehesas with nearby treeless grasslands to assess the effects of oaks on ant communities. Formica subrufa, a species associated with decayed wood, was by far the most abundant species, especially in savannahs. Taxa specialized in warm habitats were the most common both in dehesas and grasslands, as expected in areas with a Mediterranean climate. Within dehesas, the number of species was higher below oak canopies than outside tree cover. Compared to treeless grasslands, the presence of oaks resulted in a higher species richness of aphid-herding and predator ants, probably because trees offer shelter and resources to predators. The presence Citation: Gaytán, Á.; Bautista, J.L.; of oaks changed also the species composition, which differed between grasslands and dehesas.
    [Show full text]
  • Amphibians and Reptiles of the Mediterranean Basin
    Chapter 9 Amphibians and Reptiles of the Mediterranean Basin Kerim Çiçek and Oğzukan Cumhuriyet Kerim Çiçek and Oğzukan Cumhuriyet Additional information is available at the end of the chapter Additional information is available at the end of the chapter http://dx.doi.org/10.5772/intechopen.70357 Abstract The Mediterranean basin is one of the most geologically, biologically, and culturally complex region and the only case of a large sea surrounded by three continents. The chapter is focused on a diversity of Mediterranean amphibians and reptiles, discussing major threats to the species and its conservation status. There are 117 amphibians, of which 80 (68%) are endemic and 398 reptiles, of which 216 (54%) are endemic distributed throughout the Basin. While the species diversity increases in the north and west for amphibians, the reptile diversity increases from north to south and from west to east direction. Amphibians are almost twice as threatened (29%) as reptiles (14%). Habitat loss and degradation, pollution, invasive/alien species, unsustainable use, and persecution are major threats to the species. The important conservation actions should be directed to sustainable management measures and legal protection of endangered species and their habitats, all for the future of Mediterranean biodiversity. Keywords: amphibians, conservation, Mediterranean basin, reptiles, threatened species 1. Introduction The Mediterranean basin is one of the most geologically, biologically, and culturally complex region and the only case of a large sea surrounded by Europe, Asia and Africa. The Basin was shaped by the collision of the northward-moving African-Arabian continental plate with the Eurasian continental plate which occurred on a wide range of scales and time in the course of the past 250 mya [1].
    [Show full text]
  • Checklist of Amphibians and Reptiles of Morocco: a Taxonomic Update and Standard Arabic Names
    Herpetology Notes, volume 14: 1-14 (2021) (published online on 08 January 2021) Checklist of amphibians and reptiles of Morocco: A taxonomic update and standard Arabic names Abdellah Bouazza1,*, El Hassan El Mouden2, and Abdeslam Rihane3,4 Abstract. Morocco has one of the highest levels of biodiversity and endemism in the Western Palaearctic, which is mainly attributable to the country’s complex topographic and climatic patterns that favoured allopatric speciation. Taxonomic studies of Moroccan amphibians and reptiles have increased noticeably during the last few decades, including the recognition of new species and the revision of other taxa. In this study, we provide a taxonomically updated checklist and notes on nomenclatural changes based on studies published before April 2020. The updated checklist includes 130 extant species (i.e., 14 amphibians and 116 reptiles, including six sea turtles), increasing considerably the number of species compared to previous recent assessments. Arabic names of the species are also provided as a response to the demands of many Moroccan naturalists. Keywords. North Africa, Morocco, Herpetofauna, Species list, Nomenclature Introduction mya) led to a major faunal exchange (e.g., Blain et al., 2013; Mendes et al., 2017) and the climatic events that Morocco has one of the most varied herpetofauna occurred since Miocene and during Plio-Pleistocene in the Western Palearctic and the highest diversities (i.e., shift from tropical to arid environments) promoted of endemism and European relict species among allopatric speciation (e.g., Escoriza et al., 2006; Salvi North African reptiles (Bons and Geniez, 1996; et al., 2018). Pleguezuelos et al., 2010; del Mármol et al., 2019).
    [Show full text]
  • Snakebites Notified to the Poison Control Center of Morocco Between
    Chafiq et al. Journal of Venomous Animals and Toxins including Tropical Diseases (2016) 22:8 DOI 10.1186/s40409-016-0065-8 RESEARCH Open Access Snakebites notified to the poison control center of Morocco between 2009 and 2013 Fouad Chafiq1,2*, Faiçal El Hattimy2, Naima Rhalem1,2, Jean-Philippe Chippaux3, Abdelmajid Soulaymani2, Abdelrhani Mokhtari2 and Rachida Soulaymani-Bencheikh1,4 Abstract Background: Snakebites cause considerable death and injury throughout the globe, particularly in tropical regions, and pose an important yet neglected threat to public health. In 2008, the Centre Anti Poison et de Parmacovigilance du Maroc (CAPM) started to set up a specific strategy for the control of snakebites that was formalized in 2012. The aim of the present study is to describe and update the epidemiological characteristics of snakebites notified to CAPM between 2009 and 2013. Methods: This retrospective five-year study included all cases of snakebites notified to CAPM by mail or phone. Results: During the study period, 873 snakebite cases were reported to CAPM, an average incidence of 2.65 cases per 100,000 inhabitants with 218 cases each year. The highest incidence was found in Tangier-Tetouan region with 357 cases (40.9 %) followed by Souss Massa Draa region with 128 cases (14.6 %). The average age of patients was 26.8 ± 17.2 years. The male to female sex ratio was 1.67:1 and 77 % of cases occurred in rural areas. The bites occurred mainly in spring (44 %) followed by summer (42 %). Snake species was identified in 54 cases (6.2 %): colubrids represented 31 % (n = 18) and vipers 67 % (n = 36), mainly Daboia mauritanica, Bitis arietans and Cerastes cerastes.
    [Show full text]