Megafauna-Dependent Plants

How did megafauna-dependent plants survive after the demise of the giant Pleistocene seed dispersers? Before hand, be warned that coextinctions are very difficult to assess and demonstrate in nature, especially for certain groups (e.g., hosts and ectoparasites). Moreover, think of the myriad possibilities for plants to stay on place even with collapsed dispersal: just haphazard seed dispersal may help; or suboptimal fruit removal and sporadic dispersal by other, less reliable frugivores; or the dispersal being taken over by efficient frugivores (e.g., scatter-hoarders) yet with limitations in some aspect of the dispersal service (e.g., loss of long-distance dispersal events); or dispersal taken over by megafauna surrogates such as livestock; or just by relying on vegetative propagation; or maybe by just being used by humans… All these situations show up eventually when one examines the natural history details of present-day “megafauna-dependent” plants. Thus, at some point it is not surprising that documented coextinctions of plants following the loss of seed dispersers are so rare, if there is any.

Seeds of fruits from megafauna-dependent plants
Seeds of fruits from megafauna-dependent plants (the label, for scale, is ca. 11 cm long). From top left to bottom right: Pouteria ucucui (Sapotaceae), Attalea (Orbygnia) phalerata (Arecaceae), Scheelea martiana (Arecaceae), Theobroma grandiflora (Malvaceae) (two images), Pouteria pariry (Sapotaceae), Licania macrophyla (Chrysobalanaceae), Parinari montana (Chrysobalanaceae), Lacunaria jemmani (Quiinaceae), Pouteria macrocarpa (Sapotaceae), Phytelephas macrocarpa (Arecaceae), Caryocar villosum (Caryocaraceae), Theobroma sp. (Malvaceae), Raphia vinifera (Arecaceae), Lecythidaceae, and Theobroma speciosa (Malvaceae). Pedro Jordano; Museum Goeldi Herbarium, Belém, Pará, Brazil.

However, even if seed dispersal has not fully collapsed, and even if coextinctions have not been extensive, the consequences have been non-trivial for the plant species that lost their megafauna frugivores: increased clumping, increased population isolation, severily-limited gene flow via seed, loss of genetic diversity, markedly reduced effective population sizes (i.e., the number of adults effectively contributing progeny), and demographic bottlenecks. Much research is still needed to fully understand which are these “cryptic” consequences of collapsed seed dispersal mutualisms, yet there are good evidences that the demographic and population genetic consequences are non-trivial.

Collevatti, R., Grattapaglia, D. & Hay, J. (2003) Evidences for multiple maternal lineages of Caryocar brasiliense populations in the Brazilian Cerrado based on the analysis of chloroplast DNA sequences and microsatellite haplotype variation. Molecular Ecology, 12, 105–115.

Malhi, Y., Doughty, C.E., Galetti, M., Smith, F.A., Svenning, J.-C. & Terborgh, J.W. (2016) Megafauna and ecosystem function from the Pleistocene to the Anthropocene. Proceedings of the National Academy of Sciences USA, 113, 838–846.

McConkey, K.R., Brockelman, W.Y., Saralamba, C. & Nathalang, A. (2015) Effectiveness of primate seed dispersers for an “oversized” fruit, Garcinia benthamii. Ecology, 96, 2737–2747.

Hall, J.A. & Walter, G.H. (2014) Relative seed and fruit toxicity of the Australian cycads Macrozamia miquelii and Cycas ophiolitica: further evidence for a megafaunal seed dispersal syndrome in cycads, and its possible antiquity. Journal of Chemical Ecology, 40, 860–868.

Hall, J.A. & Walter, G.H. (2013) Seed dispersal of the Australian cycad Macrozamia miquelii (Zamiaceae): Are cycads megafauna-dispersed “grove forming” plants? American Journal of Botany, 100, 1127–1136.

Janzen, D.H. (1981) Enterolobium cyclocarpum seed passage rate and survival in horses, Costa Rican Pleistocene seed dispersal agents. Ecology, 62, 593–601.

Text and photos: Pedro Jordano. Seedlings and dung photos: Alicia Solana. Seed photos from Museum Goeldi Herbarium, Belém, Pará, Brazil.

Extinct Megafauna Frugivores

The diversity of extinct megafauna frugivores was extremely high in different continents, and a number of them played a central role in the evolution of fruit traits we see today. While the largest South American extant mammal is the tapir (Baird’s, up to 400 kg), consider that 100% of megamammal species (body mass >1000 kg) and about 80% of large mammal species (those over 44 kg) from the Pleistocene South American fauna was extinct ca. 10-12 Kyr BP. At least 37 genera of mammals were eliminated, including most of the megafauna species (i.e., gomphotheres, camelids, ground sloths, glyptodonts, and toxodontids). All megamammals (37 species) and most large mammals (46 species) present during the late Lujanian (latest Pleistocene- earliest Holocene) became extinct in South America (around 30 genera of mammals vanished in North America, 17 in Australia, and 24 in Asia). In contrast, Africa lost 8 of 50 megamammal genera. Africa and Southern Asia are the only continental areas that have terrestrial mammals weighing over 1000 kg today.

A number of the extinct Pleistocene megamammals were herbivores, grazers, browsers, and certainly did include fruits in their diet, probably in large amounts, thus potentially acting as seed dispersers for a variety of plants. This fact has been evidenced from coprolites and isotopic analysis of fossil remains, with additional insight from comparative anatomy and morphology. Present-day plant-frugivore interactions still have the signals of these ghosts of evolution.

Haynes, G. (ed.). 2009. American megafaunal extinctions at the end of the Pleistocene. Springer, Berlin.

Barlow, C. 2000. The ghosts of evolution: nonsensical fruit, missing partners, and other ecological anachronisms. Basic Books, New York.

Illustration: Sinammonite

Most of the species shown in this great illustration from Sinammonite ( were frugivorous (probably with the exception of the large carnivores) and legitimate seed dispersers of their food plants. The figure is high-res; you may wnat to zoom-in and seek the species names by the numbers.


Prehistoric megafauna.
1. Chilotherium anderssoni: 1.4m
2. Ancylotherium sp.: 1.8m
3. Sinotherium lagrelii: 2.6m
4. Pachycrocuta brevirostris: 1m
5. Panthera tigris: 0.97m
6. Homotherium crenatidens: 1.1m
7. Xenosmilus hodsonaei: 1.1m
8. “Amerhippusscotti: 1.5m
9. Hipparion insperatum: 1.9m
10. Loxodonta atlantica: 3.5m
11. Stegodon zdanskyi: 3.9m
12. Ningxiatherium euryrhinu: 2.2m
13. Gigantopithecus blacki: 1.8m
14. Dinocrocuta gigantea: 1.4m
15. Amphimachairodus palander: 1.1m
16. Smilodon populator: 1.2m
17. Panthera atrox: 1.3m
18. Equus sussenbornensis: 1.8m
19. Elephas maximus: 2.9m
20. Dzungariotherium orgosense: 4.5m
21. Palaeoloxodon antiquus: 4m
22. Bison priscus: 2.1m
23. Equus capensis: 1.46m
24. Elasmotherium chaprovicum 2.8m
25. Mammuthus trogontherii: 4.5m
26. Proboscidipparion sinense: 1.8m
27. Plesippus enormis 1.65m
28. Ceratotherium cottoni: 1.8m
29. Diprotodon optatum: 1.9m
30. Palaeoloxodon recki: 4.5m
31. Mammut borsoni: 3.5m
32. Equus koobiforensis: 1.6m
33. Palorchestes azael: 1.3m
34. Sivapanthera pleistocaenica: 1m
35. Equus mosbachensis: 1.65m
36. Stephanorhinus kirchbergensis: 2m
37. Palaeotherium giganteum: 1.5m
38. Zygomaturus trilobus: 1.5m
39. Deinotherium giganteum: 3.5m
40. Paraceratherium lepidum: 4.5m
41. Mammuthus columbi: 4m
42. “Equusmajor: 1.78m
43. Coelodonta antiquitatis: 1.8m
44. Bubalus youngi: 1.8m
45. Dzungariotherium? tienshanense: 5m
46. Stegodon ganesa: 4m
47. Sinohippus robustus 1.3m
48. Panthera spelaea: 1.2m
49. Embolotherium andrewsi: 2.8m
50. Allohippus sanmeniensis: 1.8m
51. Elasmotherium caucasicum: 3m
52. “Equusgiganteus: 2.25m
53. Syncerus antiquus: 1.65m


Seed dispersal by megafauna (extinct and extant)

I’ll be posting a series on megafauna (extinct and extant) and megafauna-dependent plants that I’ve been contributing to our Facebook page Frugivores & Seed Dispersal during the month of December. The posts focused on megafauna frugivores and megafauna-dependent fruits and seeds, and the processes of dispersal associated with them. I also included other interesting posts on frugivory and seed dispersal, as ever, but megafauna was the focus. Hopefully we contribute to a better appreciation of the distinct ecological roles and the contribution of megafauna species to the functioning and maintenance of ecosystems around the world, specifically on their role as frugivores and seed dispersers.


Among the most spectacular frugivores and seed dispersers we find the Megafauna species, those amazing beasts that impress every naturalist because of their adaptations, life histories, and specific traits. Yet megafauna species are being particularly hard hit by human-driven activities, notably hunting and deforestation. Megafauna species are traditionally defined as being above 40 kg body mass (i.e., > 100 lb), and include a full range of mammals (e.g., rhino, elephants, a number of antelopes, large primates), birds (e.g., ostrich, cassowary, emu), and reptiles (e.g., varanids, turtles). Moreover, think about the late Pleistocene (~12 Kyr BP) extinction of an even richest diversity of megafauna species: toxodons, terrestrial sloths, mamuths, gliptodons, gomphoteres, etc. The study of frugivory and seed dispersal (FSD) by megafauna opens a number of extremely interesting questions, ranging from the role of past history in shaping fruit traits, the lasting signatures of past extinctions of major seed dispersers for plants (e.g., in the genetic pools), the conflicts and interactions with humans in natural and seminatural habitats, the role of extremely long-distance seed dispersal by megafauna and its collapse following extinction, etc.

Illustration: Dadi, “Cada um”.


Our study on functional extinction of frugivores, published in Science

Our new paper “Functional Extinction of Birds Drives Rapid Evolutionary Changes in Seed Size”, just published in this week issue of Science.

Mauro Galetti, Roger Guevara, Marina C. Côrtes, Rodrigo Fadini, Sandro Von Matter, Abraão B. Leite, Fábio Labecca, Thiago Ribeiro, Carolina S. Carvalho, Rosane G. Collevatti, Mathias M. Pires, Paulo R. Guimarães Jr., Pedro H. Brancalion, Milton C. Ribeiro, and Pedro Jordano. 2013. Functional Extinction of Birds Drives Rapid Evolutionary Changes in Seed Size. Science 340: 1086-1090.
DOI: 10.1126/science.1233774.

Palmito collage large

Photos, from top left, descending, to right:

1. Selenidera maculisrotris (male) handling a palmito seed.
2. Palmito fruits with beak marks, dropped beneath the palm, and regurgitated seeds.
3. Turdus flavipes trying to swallow a palmito fruit.
4. Ramphastos vitellinus (subsp. vitellinus) handling a fruit.
5. Selinedera maculirostris (male) picking a fruit.
6. Palmito seedling just after germination (note the seed still attached).
7. Palmito juçara, Euterpe edulis (Arecaceae).
8. Aburria (Pipile) jacutinga.
9. Baillonius (Pteroglossus) bailloni handling a fruit.
10. Turdus amaurochalinus (young), picking a fruit.
11. View of the ompbrphilous atlantic rainfrorest (Mata Atlántica) understory in Carlos Botelho park.
12. Penelope obscura.
13. Pyroderus scutatus, swallowing a fruit.
Photos by: Edson Endrigo, Pedro Jordano, Mauro Galetti, Marina Cortes, Guto Balieiro, and Lindolfo Souto.

The selective extinction of large frugivorous birds is associated with the rapid evolutionary reduction of seed size in a keystone palm.

Local extinctions have cascading effects on ecosystem functions, yet little is known about the potential for the rapid evolutionary change of species in human-modified scenarios. We show that the functional extinction of large-gape seed dispersers in the Brazilian Atlantic forest is associated with the consistent reduction of seed size of a keystone palm species. Among 22 palm populations, areas deprived of large avian frugivores for several decades present smaller seeds than non-defaunated forests, with negative consequences for palm regeneration. Coalescence and phenotypic selection models indicate that seed size reduction most likely occurred within the last 100 years, associated with human-driven fragmentation. The fast-paced defaunation of large vertebrates is most likely causing unprecedented changes in the evolutionary trajectories and community composition of tropical forests.

When we talk about biodiversity we normally refer to the number of species found in a given area. But these species have ecological functions that are essential to the functioning of ecosystems. The loss of a species also entails the loss of the ecological role it plays in the ecosystem, and this kind of extinction happens much unnoticed. We have documented the effect of functional extinction of large fruit-eating birds on an important plant trait – seed size – of a key plant species of the Atlantic Rainforest in Brazil, one of the biodiversity “hot-spots” on the planet. Our study is a natural experiment that takes advantage of the presence of fragmented areas of forest that have remained so since the early 1800s, when the development of crops such as coffee and sugar cane triggered the extensive deforestation of the Atlantic rainforest. Only 12% of the original forest persists, and over 80% of what remains are fragments are too small to maintain large animals. Our results show that the loss of large fruit-eating birds such as toucans leads to the size reduction of the seeds of a palm tree, which is a key species in these Atlantic forests. These evolutionary changes in fruit and seed size have occurred only in defaunated forests, where only small frugivorous birds persist. These small birds only successfully disperse smaller seeds.

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We studied 22 populations of this palm tree along the SE coast of Brazil. In the defaunated areas, which persist as fragments from several decades ago, the seed sizes are consistently smaller than in well-preserved forests, and this has negative consequences for regeneration. The smaller seed size in defaunated areas is not explained by other environmental or geographic variables. Fast natural selection: Small birds such as thrushes cannot swallow and disperse large seeds. Large birds, such as aracaris and toucans, play an important role in dispersing seeds of plants, especially of large seeds. In rainforests without toucans large seeds tend to disappear over time because undispersed seeds are attacked by seed predators. Small seeds are more vulnerable to desiccation and cannot withstand projected climate change.

We have combined a number of techniques including field work, genetic analyses, evolutionary models and statistical analyses. We collected ground data on a large number of palm trees in 22 populations, by collecting fruits, observing the avian frugivore assemblage and conducting germination experiments. We have also used DNA genetic markers to employ quantitative genetic models to estimate the intensity of selection on seed traits and coalescence theoretical models to infer the time of isolation of populations. Finally, we statistically analyzed the effect of different types of data, including climatic and environmental information, on seed size variation. 

Our work provides one of the few existing evidence that evolutionary change in natural populations can happen very fast as a direct result of changes induced by human action. The extinction of large vertebrates is happening all over the world and the implication is poorly known. These large bodied species maintain mutualistic interactions with plants: while flesh-fruited plants offer fruits as food sources, frugivores disperse their seeds. Such ecological process ensures natural regeneration of the forest. Unfortunately, the effect we document in our work is probably not an isolated case. The constant extirpation of large vertebrate in natural habitats is very likely causing unprecedented changes in evolutionary trajectories of many tropical species.

Habitat loss and species extinction is causing drastic changes in the composition and structure of ecosystems. This involves the loss of key ecosystem functions that can determine evolutionary changes much faster than we anticipated. Our work highlights the importance of identifying these key functions to quickly diagnose functional collapse of ecosystems.

Components of pollination effectiveness and their consequences in insular pollinator assemblages

Our paper “Quantity and quality components of effectiveness in insular pollinator assemblages” online in Oecologia. Thanks Cande and Alfredo. This is a field study of the pollination of Isoplexis canariensis by birds and lizards in the Canary Islands, a part of Cande Rodríguez PhD project.

Ecologically isolated habitats (e.g., oceanic islands) favor the appearance of small assemblages of pollinators, generally characterized by highly contrasted life modes (e.g., birds, lizards), and opportunistic nectar-feeding behavior. Different life modes should promote a low functional equivalence among pollinators, while opportunistic nectar feeding would lead to reduced and unpredictable pollination effectiveness (PE) compared to more specialized nectarivores.

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Dissecting the quantity (QNC) and quality (QLC) components of PE, we studied the opportunistic bird–lizard pollinator assemblage of Isoplexis canariensis from the Canary Islands to experimentally evaluate these potential characteristics. Birds and lizards showed different positions in the PE landscape, highlighting their low functional equivalence. Birds were more efficient than lizards due to higher visitation frequency (QNC). Adult lizards differed from juveniles in effecting a higher production of viable seeds (QLC). The disparate life modes of birds and lizards resulted in ample intra- and inter-specific PE variance. The main sources of PE variance were visitation frequency (both lizards and birds), number of flowers probed (lizards) and proportion of viable seeds resulting from a single visit (birds).

The non-coincident locations of birds and lizards on the PE landscape indicate potential constraints for effectiveness. Variations in pollinator abundance can result in major effectiveness shifts only if QLC is relatively high, while changes in QLC would increase PE substantially only at high QNC. The low functional equivalence of impoverished, highly contrasted pollinator assemblages may be an early diagnostic signal for pollinator extinction potentially driving the collapse of mutualistic services.

University of Sevilla PhD award for Francisco Rodríguez

The University of Sevilla has awarded Francisco Rodríguez with the PhD Excellence Award, 2012. Paco carried out his PhD project in the lab, working on dispersal ecology of Laurus nobilis. Big congratulations Paco!!!

Moving to WordPress

I’m about to complete the moving of my blog (started by early 2003…) to WordPress. There are several reasons for this- the most important being the ability to edit from the tablet and phone, and better versatility with the editing and composition of entries. I keep using iWeb and Dreamweaver for the web page, however, at least until iWeb is discontinued by Apple. The older version of the blog is here. The new blog in WP is called “The Red Notebook“.

Megafauna fruits and seeds photos updated

I’m in the process of moving photo repositories to iCloud and have my previous photos of megafauna fruits and seeds moved to this gallery. You can access the photos here.

These photos were taken in the herbarium of Museu Goeldi (Belém, Pará, Brazil) in 2002. They include many of the species we discuss in our paper in PLoS One on megafauna fruits.

Lizards, endemic island plants and extinctions

Seed dispersal by lizards is an insular phenomenon. In the Canary Islands, many fleshy-fruited plants depend on lizards for their successful dispersal and recruitment. We are now working in a project directed by Alfredo Valido to analyze the movement ecology of Canarian endemic Gallotia lizards and its consequences for plant dispersal and recruitment. We study the reproductive ecology of orijama plants Neochamaelea pulverulenta, an endemic Cneoraceae in the islands, whose seeds are exclusively dispersed by the lizards. We combine studies of fine- and medium-scale genetic structure with data and models of foraging movements of the lizards, monitoring with radio-tracking methods. So far the results are superb, and we now have detailed data on movement patterns of Gallotia galloti in Teno Bajo (Tenerife)- our main study site- and G. stehlini (in the photo) in Barranco de Veneguera (Gran Canaria). We have also seeds samples from two 1.2 ha plots in the two sites as well as leaf samples from >2000 plants to assess seed dispersal patterns with genetic methods, similar to those that we’ve been using with Prunus mahaleb and Frangula alnus. We are interested in assessing the potential effects of previous extinctions of other giant lizard species (e.g., G. goliath) that were very good dispersers of orijama. These were up to 1.3 m long and able to disperse even the largest fruits and seeds of orijama, which now remain undispersed on the plants; only the smaller fruits and seeds remain dispersed by the extant smaller lizards.

Number One

This is my note #1. Created 01/01/2011 @ 00:35. Really a few minutes after the Biodiversity year has ended. What do we have? Probably a few thousands more extinct species, many of them we yet don’t know. But we have also more knowledge to fight this fast-paced trend of biodiversity loss. Let’s hope the best…

I have imported my previous posts of my blog.

PhD thesis defense by Débora Rother

  PhD thesis defense by Débora Rother: “ Débora defended her thesis at UNESP (Rio Claro, Brazil) the 30th Nov. The thesis is entitled: ‘Dispersão de sementes e processos de limitação demográfica de plantas em ambientes com e sem bambus na floresta pluvial Atlântica’. She addressed the patterns of regeneration in the Atlantic rainforest of SE Brazil by combining observational studies of seed rain and seedling emergence and experimental seed addition. She studied Euterpe edulis, Sloanea guianensis, and Virola bicuhyba. The dispersal patterns of these species and their regeneration are deeply influenced in this forest by the presence of bamboo (Guadua tagoara) stands. This heterogeneity causes variation in the composition of the frugivorous avifauna and the density of seeds and established seedlings. She addressed the specific demographic transitions from dispersed seed to established saplings that can limit the natural regeneration of these forests. Bamboo stands influenced seed rain patterns in the complex mosaics of Atlantic rainforest areas, with a variable importance across seasons on the abundance of recruits and species richness of the seed rain. Besides, the hotspots of recruitment were shown as extremely dynamic and related to the spread and decline of G. tagoara stands. Bamboos promote the forest heterogeneity, but the characteristics of rapid colonization of G. tagoara and its invasive behavior can be one additional factor for limiting the growth of plant community and thus its management is important.
The defense went very well and she has already in press or submitted manuscripts of several chapters. Congratulations Dé for an excellent work!”

(Via Weblog de Pedro.)

Starting fieldwork in Teno Bajo

  Starting fieldwork in Teno Bajo: “ We (Alfredo, Néstor and myself) are this week with field work in Teno Bajo (Teneriffe), finishing georreferencing and sampling of orijama (Neochamaelea pulverulenta) plants in the study plots. The work is going fine in this spectacular site. We study seed dispersal by the Gallotia endemic lizards to analyze the consequences of this specialized dispersal system on the genetic structure of the plant.” (Via Weblog de Pedro.)


Web page updates

I’ve updated the web page with new information about the research lines at the lab, projects, and personnel. This includes brief descriptions of the main research lines, collaborations, etc. All are accesible from the Research web page under Research Lines.

Some updates after summer

After summer

Well, it has been a long time without news in the blog, but here we are again. 😉 Summer has been quiet; I’ve been at Cadiz coast with Myriam and Perico, with a short visit by Diego. It has been a great time to read, think and write but, again, no painting at all… 😦
After summer the group has been plenty of news. Geno Schupp and Janis Boettinger arrived in Sevilla for a new sabbatical year. We have plenty of time ahead to start new projects and revisit old ideas, besides enjoying the ‘tapas’ landscape around us.
We (Jordi, Jens and myself) got the Mercer Award of the Ecological Society of America for the Science paper; and Jordi, Jessica and Miguel Angel went to the meeting in San Jose (California) and enjoyed a splendid ceremony. This award is in recognition for the paper in Science (2006) on interaction asymmetries in mutualistic networks.
We have a new incorporation of Rocío Rodríguez, to start her PhD project on long-distance seed dispersal in Laurus nobilis and Frangula alnus. In addition, Itziar Sarasa also arrived to the group for a short-term stay until December with an introductory grant from CSIC.
Additional good news include the new grant-contracts that Arndt Hampe and Kimberly Holbrook obtained for the next 2 years in the group. Arndt is getting back to work on relict oak populations and Kimberly will keep going with the genetic analysis she started with Virola for her PhD, within a comparative project with Prunus.
Now I’m concentrating on the revision of the megafauna paper with Paulo and Mauro as well as in mss with Alfredo and Martin (fruit colors) and Jordi and Jens (networks); besides there is pending work with Geno on dispersal effectiveness and dispersal limitation that we want to finish. We really have a lot of things going on here, all great fun.

Pre-doctoral grant available

Pre-doctoral grant available

La convocatoria de ayudas para becas predoctorales FPI está próxima a ser publicada por el MEC.

Dentro de nuestro proyecto “DISPERSIÓN DE SEMILLAS POR ANIMALES FRUGÍVOROS: EVENTOS A LARGA DISTANCIA Y REDES DE CONECTIVIDAD EN POBLACIONES FRAGMENTADAS” (CGL2006-00373), estamos interesados en recibir candidaturas para una beca FPI del MEC para desarrollar una Tesis doctoral.

En plantas en las que los animales influyen directamente en el flujo génico via polen y semillas, la variabilidad genética aparece fuertemente estructurada a diferentes escalas espaciales. El mantenimiento de esta estructura espacial se basa en la conectividad entre poblaciones via polen y semillas, distribuidas por animales mutualistas. En escenarios de fragmentados es esencial comprender cómo se estructura esta conectividad a fin de poder predecir los efectos de pérdida (extinción local) de poblaciones y limitación de los procesos de dispersión. En este proyecto abordamos estos aspectos centrándonos en especies forestales amenazadas o relictas, para las cuales ya disponemos de información a raíz de proyectos anteriores. En esta propuesta abordamos el problema de la persistencia de las poblaciones de estas especies basándonos en una mejor comprensión de la conectividad que existe entre ellas y de la dependencia de animales polinizadores y frugívoros para el reclutamiento. Nos centraremos en Olea europaea var. sylvestris, y abordaremos también aspectos demográficos y genéticos en Frangula alnus, Laurus nobilis, y Prunus mahaleb. Nuestra propuesta sintetiza las principales líneas de trabajo que mantiene nuestro grupo y aborda cuestiones clave sobre la preservación de la biodiversidad de especies, interacciones y acervo genético en escenarios de cambio ambiental. El enfoque es interdisciplinar, aunando diferentes aproximaciones (análisis estadístico de bases de datos, teoría de redes complejas, métodos de genética molecular y simulaciones de ordenador).

El trabajo de tesis se centraría en los aspectos de conectividad en poblaciones fragmentadas. Perfil requerido: formación en biología y/o ciencias ambientales con un buen expediente académico. Se valorarán positivamente los conocimientos en ecología, genética molecular y estadística, con una fuerte motivación e interés por estos temas. Se requiere inglés hablado/escrito con nivel alto. El trabajo previsto incluye tareas de campo y de laboratorio.

Las bases de la convocatoria serán publicadas próximamente por el MEC (ver para convocatorias anteriores).

Las personas interesadas deben ponerse en contacto lo antes posible con Pedro Jordano adjuntando su CV actualizado (con datos de contacto) junto con copia de su expediente académico. El plazo de la convocatoria, que se publicará en BOE en breve, será sólo de unos 15 días. Más información sobre el grupo de investigación y sobre nuestro trabajo se puede encontrar en las páginas web:>>