I work in evolutionary ecology to identify and understand selection
pressures on populations. Much of my research focuses on the roles of
phenotypic plasticity and local adaptation in explaining life history traits variations
according diverse habitats, using amphibians as models (Pelophylax complexes, Rana
temporaria), but also nematode parasites used to tack host movements (Ashworthius sidemi, Spiculopteragia spiculoptera, Oesophagostomum sp). Hence, I use an ecological
and experimental approaches combined with molecular biology on wild populations
in order to study intra-specific variations along a latitudinal gradient, and
to compare life history traits among populations originating
from different habitats to dissociate local adaptation from phenotypic
plasticity.
Post-Doctoral Project at the University of Reims Champagne-Ardenne (URCA), France: Parasites used as a management tool: tracking nematodes in wild populations of roe deer to infer contacts and map the social network.
Post-Doctoral Project at the University of Reims Champagne-Ardenne (URCA), France: Parasites used as a management tool: tracking nematodes in wild populations of roe deer to infer contacts and map the social network.
Currently, I’m
working in VECPAR team at the University of Reims Champagne-Ardenne (URCA) under the supervision of Hubert Ferté and in collaboration with the
team URCA-CERFE on “IN SITU” project, which aim is to study the ecological
connectivity of mammals from Champagne-Ardenne region. In “IN SITU”, my mission
is to study population structure of parasite community of roe deer (Capreolus capreolus) in order to
evaluate direct and indirect (exploitation of the same area at different time)
contacts between populations.
Hence, we are particularly
interested in two
species of parasitic
nematodes located
in strongyles wild deer and belonging to different
taxonomic groups, Spiculoptéragia spiculoptera (Trichostrongylidae) and Oesophagostomum venulosum (Strongylidae). This
innovative approach that uses the parasites as biological
tracers will be
coupled with the study
of the population
structure of mammalian hosts, and spatial modeling performed by partners
of SITU project, to highlight the existence of biological
corridors for each species of
mammals in the
region.
In parallel, I am involved in a second project led by Hubert Ferté studying parasite prevalence of Alaria alata (Trematode) in water frogs (Pelophylax sp.) and “brown” frogs (Rana sp.). The objective here is to observe the prevalence of this parasite in different species of amphibians infected (taxonomic identification based on morphological and molecular analyzes), but also to assess which stages of these amphibians are the more sensitive to parasitic infestation.
Collaborators: Hubert Ferté (URCA), Damien Jouet (URCA), Rémi Helder (CERFE)
Post-Doctoral Project at the
University of Helsinki, Finland: Sex-reversals in the common frog (Rana
temporaria) from Lapland.
The common frog (Rana temporaria) is a small
amphibian which is widespread in Europe, and
it is the only amphibian species that has managed to adapt to subarctic
climatic conditions. As such, the northern populations of common frogs –
genetically distinct from their southern conspecifics (e.g. Laugen et al. 2001;
Palo et al. 2003; Matsuba & Merilä 2006) – can viewed to represent a unique
intraspecific level of biodiversity that we should strive to preserve.
Previous studies in EGRU of common frogs in Kilpisjärvi
(Lapland, Finland) have revealed peculiar sex
ratio dynamics: there are many more adult females than males in these northern
populations (Alho 2004, 2008, Merilä, Herczeg & Alho, 2008). Possible
explanations for this sex ratio bias include sex differences in early life
mortality, and/or sex-reversals caused by some environmental factors. Utilizing
sex-linked genetic markers, Alho et al. (2010) compared the genetic-sex with
the phenotypic-sex of Kilpisjärvi frogs and observed 9% mis-matches. This result
– which evoked great international interest (e.g. Perrin 2010) – supports the
hypothesis that sex-reversals are occurring in Kilpisjärvi.
Sex determination mechanisms in vertebrates range from
genetic sex determination (GSD; e.g. mammals, birds) involving sex chromosomes,
to environmental sex determination (ESD; e.g. many reptiles, few amphibians;
Wallace et al. 1999, Sarre et al. 2011). In ESD, the sex of the individual is
determined by environmental conditions experienced during early development.
However, sex determination of some organisms is under the influence of both
genotypic and environmental effects, and their phenotypic sex is determined by
the interaction of these two factors (Baroiller et al. 2009). For example, an
individual’s genetically determined sex can be environmentally reversed during
ontogeny, a phenomenon known as environmental sex reversal (ESR; occurs in many
fishes and amphibians; Stelkens & Wedekind 2010).
Environmental factors capable of influencing sex
determination include temperature, pH, and environmental contaminants (Figure
1) (Wallace et al. 1999, Hayes et al., 2002, Petterson & Berg, 2007, Olmstead
et al. 2009). Even social conditions experienced as juveniles are known to
influence sex-determination (Wallace et al. 1999), but clearly, more
experiments exploring the occurrence of environmental sex determination in
amphibians is needed.
I joined in 2011 the Ecological Genetics Research Unit
(EGRU) at the University of Helsinki to follow this research project
on sex-reversal phenomenon of common frogs under the supervision of Pr. Juha Merilä.
First, I led a field expedition at the Biological Station of Kilpisjärvi in
Northern Lapland (Finland)
to monitor the isolated population of common frogs and to collect DNA and
tissues samples, in order to evaluate the population situation which was
observed between 1998 and 2004, and assess the persistence of sex-reversed
individuals, phenomenon already observed in this region. In a second step, I
observed age structure, body size and growth range of these common frogs to
assess the effect of extreme environmental conditions on the activity of this
species. Then, I work on the development of sex-linked molecular markers using
reads from Next-Generation-Sequencing analysis to identify the genotypical sex
of common frogs. Finally, I contributed to RACE project (Risk Assessment of
Chytridiomycosis to European Amphibian Biodiversity), proceeding to the
screening of chytrid fungus of these isolated common frogs from Northern Finnish
Lapland.
Collaborators: Juha Merilä (University of Helsinki), Jussi Alho (University of Helsinki), Anssi Laurila (University of Uppsala), Mårten Hjernquist (University of Uppsala), Fredrik Soderman (University of Uppsala).
Articles n°3 and n°4
PhD thesis at the University
of Angers, France: "Hybridization complexes in European water frogs:
genetic identification, ecological constraints, and adaptation abilities"
Hybridization is receiving renewed attention as hybrid
zones are known to be places where important evolutionary events occur.
(Arnold, 1997; Rieseberg, 1997; Barton, 2001; Baack & Rieseberg, 2007).
Defined as interbreeding between differentiated lineages or taxa, interspecific
hybridization events occur in almost all sexually reproducing groups of
organisms (Seehausen 2004, Mallet 2005), and are regular and probably important
in nature {Seehausen, 2004). Long-term consequences of hybridization depends on
the genetic basis of hybrid fitness, include fusion of previously distinct
lineages, extinction of one or both lineages, evolution of reproductive
isolation via reinforcement, and production of novel, highly fit hybrid
phenotypes (Lippman, 2007). This hybrid vigour is due to the heterosis effect
(because of higher heterozygotie rate), which confers advantages to increased
genetic diversity (Moore 1977, Tunner and Nopp 1979), and can permit hybrid
lineages to colonize new niches or allow speciation through parallel selection
pressures and divergent natural selection (Parris et al. 1999, Rieseberg et al.
2003, Rhode and Cruzan 2005, Fitzpatrick and Bradley Shaffer 2007); (Gross and
Rieseberg 2005, Robbins et al. 2010). Thus, natural hybridization event is an admixture
which can create
new phenotypes allowing a great phenotypic plasticity and facilitates
adaptive evolution in modified or degraded habitats (Rieseberg et al. 2003,
Johansen-Morris and Latta 2008).
Among hybridization events, unisexual hybrids
constitute a peculiar case in evolutionary ecology especially interesting to
study the adaptation processes. These hybrid lineages are resulting from
crosses between differentiated bisexual species, and stabilising through a
clonal (parthenogenesis, gynogenesis) or hemiclonal (hybridogenesis)
reproductive mode (Vrijenhoek 1993). They are generally thought to be
evolutionary ‘dead-ends’ (Maynard Smith 1978, Simon et al. 2003), but the
persistence of stable unisexual lineages in numerous independent taxa,
sometimes ancient, contradicts this generality (Judson & Normarck, 1996;
Normack et al., 2003). As an example, stable unisexual hybridogenetic/bisexual
complexes have been observed in fishes (Poeciilidae and Cyprinidae), insect
(Phasmatodae and Chironomidae, and amphibians (Ranidae) (Schultz 1969, Berger
1973, Tinti et al. 1995, Collares-Pereira et al. 1999).
In these hybridogenetic complexes, gametogenesis is characterized by
distortion prior to meiosis leading to genome exclusion of one parental species
in the hybrid germ line, and by the production of clonal gametes which only
contain the genome from the other parental species without recombination
(Schultz 1969). The hybridogen generally reproduce, as a sexual parasite, with
the parental species from which the genome is discarded, for maintaining at
each generation its lineage (Graf and Polls Pelaz 1989, Beukeboom and
Vrijenhoek 1998, Holsbeek et al. 2008). Mating between hybrids produce
non-hybrid offspring possessing two hemiclonal genomes, and often die at an
early larval stage, because they express recessive deleterious mutations
(Binkert et al. 1982, Semlitsch and Reyer 1992, Guex et al. 2002).
European water frogs (Amphibia: Ranidae) are characterized by several
hybridogenetic complexes (Graf and Polls Pelaz 1989). “Pelophylax esculentus complex” is the most widespread and abundant
complex, occurs in Central and Eastern Europe,
and involve:
- the parental species P. ridibundus (genome RR) Pallas, 1771,
- P. lessonae (genome LL) Camerano, 1882,
- and the hybridogen P. kl.
esculentus (genome RL) Linnaeus, 1758.
These hybrids are characterized by a hybridogenetic reproduction mode (Schultz 1969): the genome of P. lessonae is eliminated from the germline prior to meiosis, and
the genome of the other parental species, P.
ridibundus, is clonally transmitted through gametes to the next hybrid
generation. Indeed, the hybridogens, considered as a unisexual organisms, usually
coexist with P. lessonae, the sexual
parental host species, on which depends the restoration of hybrid lineages
(named L-E system) (Uzzell and Berger 1975).
Another hybridogenetic complex occurs in Southern France and Northern
Spain, “P. grafi complex” (Graf et al. 1977, Graf and Polls Pelaz 1989, Pagano
et al. 2001c, Daf et al. 2006). In the P-G system,
analogous to the L-E system:
- P.kl. grafi (genome RP) is
the hybrid between
- P. perezi Seoane, 1885 (genome PP),
- and P. ridibundus.
Hybridogenetic lineages produce only haploid gametes with ridibundus genome, and restore at each
generation through matings with P. perezi
(Graf and Polls Pelaz 1989).
Strongly interesting in evolutive ecology and by the complexity of this
group of amphibians, I began my PhD in 2007 in collaboration with
two research units, the “Centre de Recherche et de Formation en Eco-Ethologie”
(CERFE, France) and “Laboratoire d’études des Systèmes Anthropisés”, Université
d’Angers (LEESA, France). I was co-supervised by Alain Pagano, Professor Associated at the University of Angers, and Remi Helder, Research Engineer at CERFE, University of Reims. My PhD focused
on these two hybridogenetic complexes of
water frogs in the Ardennes (Northeast part of France),
in Bretagne and Pays de la Loire (Northwest
part of France) and in
Northeast part of Spain).
Aims of this project were:
i) to identify the different taxa of these complexes
using new molecular tools (Allozymes, PCR-RFLP method on ITS2,
microsatellites),
ii) to analyse of environmental effects on taxonomic
distribution (aquatic and terrestrial parameters) and ecological constraints
iii) and to evaluate habitat effect on
life-history traits and larval performances of tadpoles through
experimental breeding.
A new PCR-RFLP-based method for an easier systematic affiliation of European water frogs
We developped a non-invasive,
PCR- RFLP based method that allows reliable determination of the European water
frog species Pelophylax lessonae
and P. ridibundus and the hybrid form
P. esculentus. Maximum likelihood
analysis of ITS2 sequences revealed two robust monophyletic clades
corresponding to parental species. Three restriction enzymes (KpnI, HaeII,
SmaI) were used to digest three
conserved ITS2 domains. Taxonomic identification was unambiguous, the three
restriction enymes gave the same results. The protein electrophoretic method of
identification was carried out on a French reference sample to test its
efficiency. Our new method confirmed circa 83% of identification of the old
one. We concluded that difference between identifications was due to
introgression.
Collaborators: Torsten Ohst (Museum für Naturkunde), Jörg Plötner (Museum für Naturkunde)
Article n°1, Mol Ecol Res
Heterosis and clonal genome
effects in water frog hybrid complexes: A preliminary attempt at measuring
their respective implication.
Unisexual hybrids may combine heterosis and accumulation of deleterious
mutations. This contrasting advantages and disadvantages question the fate of
these lineages. As waterfrogs constitute hybridogenetic complexes where
hemiclonal hybrids occur, we aim to compare the performances of distinct tadpole
lineages (hybrid or non hybrid but bearing a clonal genome). In a first step,
we compared the fitness-related larval life-history traits (survival and growth
rates, time to metamorphosis and mass at metamorphosis) evidencing an
intermediate performance of hybridogenetic tadpoles P. kl. grafi in
comparison with the parental species. In a second step, we compared the
performances of P. ridibundus tadpoles
with different genomes: either containing 100% sexual genomes or 50%. No strong
differences were observed among lineages, suggesting few effect of mutation
accumulation except for the RRg lineage that exhibited a bad performance, may
be due to a more ancient clonal history. Our data suggest that P. ridibundus
tadpoles are more competitive than other southern water frog, and represent
a risk for the diversity of indigenous water frog assemblages in France and Spain.
Collaborators: Gaston-Denis Guex (University of Zürich), Thomas Uzzell (Academy of Natural Science)
Article n° 6 (Submitted)
Distribution and niche partition
Water frogs from the complex P. esculentus was
investigated in the Ardennes department (14
sites) in 2007 and the Maine-et-Loire in 2008 (12 sites) to refine our
understanding of the ecological requirements of different taxa (Morand &
Joly 1995). The observed pond were located in different habitats and in areas influenced
differently (from pond directly connected to the river to the pond in meadow at
the top of hill). Each site has been characterized (physicochemical parameters,
land use), and frogs were caught momentary to study species composition. Thus,
among the 759 individuals captured, the composition was significantly different
between two regions, the Ardennes containing
essentially P. lessonae and hybrids, while Maine-et-Loire was mainly composed
of P. ridibundus and hybrids. We confirmed a differential use of habitat
between the parental species of frogs of the complex P. esculentus, supporting
the hypothesis of ecological niche partition (Pagano et al., 2001, Plénet et
al. 2000), and observed correlations with new factors influencing their
abundance: P. ridibundus is present in grassland habitats with a strong river influence,
then a short distance from the river, at low altitudes, in water few turbid and
low in nitrates; P. lessonae is more present in forest environments with low
impact river, at a greater distance from the river and at higher altitude,
rather basic pH. In contrast, the hybrid is present in all ponds, sometimes in
sympatry with P. ridibundus, sometimes with P. lessonae, or with both,
revealing the large ecological valence of this ubiquitous group. Its abundance
is correlated to the same parameters as P. lessonae, but it seems to support
environments containing nitrates.
Evolutionary
success of hybrids: Larval
performance variations of water frogs Pelophylax
klepton esculentus tadpoles from
different habitats
Hybrid zones
are known to be places where important evolutionary events occur. Having
observed a very broad
distribution of hybrids, we
investigated intra-specific variability of water frog hybrids in response to
their environmental modifications. We examined through six crosses (forest,
meadow, or mixed origins) the potential effect of habitat of origin on larval
development of Pelophylax klepton esculentus tadpoles. We thus exposed
them to 20°C
and 26°C
rearing conditions, temperatures similar, respectively, to those recorded in a
field survey of forest and meadow habitats. Tadpoles raised at 26°C had a better survival and
growth rates, a smaller size and quicker metamorphosis than those raised at 20°C. Larval performances
varied regarding habitat of origin of tadpoles : forest tadpoles survived
better, were smaller and metamorphosed earlier than those from meadow at 20°C. However meadow and mixed
tadpoles had a better proportion of survivors at 26°C. P. kl. esculentus tadpoles
had different larval performances according to their habitat of origin. Because
they exhibited a better survival rate, forest tadpoles had a higher phenotypic
plasticity than meadow ones. It suggests a local adaptation of meadow tadpoles
to their habitat. Therefore, the evolutionary success of these widespread
hybrids might be due to the existence of several different lineages.
Collaborators: Audrey Chaput-Bary (MNHN Paris), Olivier Pays (University of Angers)
Article n°5 (Submitted)