Dynamique éco-évolutive de deux ascidies congénériques et interfertiles, l'une indigène et l'autre introduite, dans leur zone de sympatrie

Human activities severely alter species ranges that have been built on evolutionary time scales, and biological introductions promote secondary contacts between non-reproductively isolated species that were in allopatry. Such a situation is a very interesting case-study to examine eco-evolutionary processes, for instance coexistence between species sharing the same ecological niche or inter-specific gene flow (i.e. hybridization and introgression) between native and non-native species. This PhD thesis studied ecological and genomic interactions between two biologically similar, interfertile and congeneric tunicates, namely Ciona robusta and Ciona intestinalis. They are both abundant in harbours and marinas. They are sympatric in the Western English Channel because of the recent introduction of C. robusta (putatively native to Asia) in the natural range of C. intestinalis. Based on spatial and temporal (seasons and years) adult abundance data and examination of recruitment patterns of the two species, we showed that the two species are sustainably coexisting at a regional scale in Brittany, within similar communities. They live in syntopy in most of the study marinas. However, there are significant changes in their relative abundance through time: C. robusta is mostly present at the end of the summer and in the autumn, although always being less abundant than its native congener. Syntopy, interfertility between the two species and synchronous sexual maturity all indicated a high likelihood of hybridization between the two species. The realized hybridization is however very low, as shown by 4 species-diagnostic molecular markers genotyped over more than 3000 individuals: only 4% of the individuals displayed a genotype compatible with hybridization or introgression. This result has been confirmed with a population genomics study (310 SNPs; 450 individuals collected worldwide): inter-specific gene flow is very low. In addition, the few loci showing shared polymorphism displayed variable introgression rates and introgression was observed even in allopatric localities (where only one of the two species exists nowadays). Overall, the genetic and genomic results indicate that interspecific gene flow is most likely due to past introgression events (that may have occurred during the Pleistocene). Finally, a study carried out at a worldwide scale with two mitochondrial loci, showed that the introduction processes of C. robusta are different among the introduced regions. This study also questions the non-native status of the two Ciona species in some regions. This work showed the near absence of contemporary hybridization between C. robusta and C. intestinalis, even in syntopy, opening new research perspectives about the mechanisms preventing their reproduction in the wild. It also questions the fate of these two competing species; this competition may depend on the interaction between their specific environmental preferences and on on-going climatic changes in the North Atlantic. Altogether, this work illustrates the interplay between contemporary and past processes on species distribution and evolution, population genetic structure and genomic architecture.Les activités humaines sont à l’origine de profondes modifications de la distribution naturelle des espèces. Les introductions d’espèces sont en particulier à l’origine de contacts secondaires entre espèces non isolées reproductivement et ayant divergé en allopatrie. Cette situation est un cas d’étude particulièrement intéressant pour étudier des processus éco-évolutifs, tels que la coexistence d’espèces occupant de même niches écologiques ou les flux de gènes contemporains (i.e. hybridation et introgression) entre espèces indigènes et non-indigènes. Cette thèse s’est ainsi intéressée aux interactions écologiques et génomiques entre deux ascidies congénériques et interfertiles, Ciona robusta et Ciona intestinalis. Ces deux ascidies, abondantes dans les habitats portuaires, sont en sympatrie en Manche Occidentale suite à l’introduction récente de C. robusta (supposée originaire du Pacifique Nord-Ouest) dans l’aire de distribution naturelle de C. intestinalis. Par une étude de la distribution spatiale et temporelle (inter-saisonnière et inter- annuelle) des adultes des deux espèces et de la sédentarisation de leurs juvéniles, nous avons montré que les deux espèces coexistent de façon durable, au sein de communautés similaires, à l’échelle régionale. Elles vivent en syntopie dans la majorité des habitats portuaires étudiés, bien qu’il existe une importante dynamique saisonnière de leur abondance relative : C. robusta est surtout présente en fin d’été et en automne, et toujours en moindre abondance par rapport à sa congénère indigène. Cette syntopie, l’interfertilité des deux espèces et le synchronisme de leur maturité sexuelle indiquent un potentiel d’hybridation important entre les deux espèces. L’hybridation réalisée est pourtant faible, comme montré avec quatre marqueurs moléculaires diagnostiques des deux espèces, analysés sur plus de 3000 individus : seulement 4% des individus présentent des génotypes compatibles avec de l’hybridation ou de l’introgression. Ces résultats ont été complétés par une étude de génomique des populations (310 marqueurs SNPs et 450 individus collectés dans différents océans) : ils confirment que les flux de gènes interspécifiques sont très rares. Par ailleurs, les rares locus présentant du polymorphisme partagé montrent un taux d’introgression hétérogène, et l’introgression est également observée dans des localités où seule l’une des espèces existe (ex. côtes américaines et chiliennes). L’ensemble des résultats génétiques et génomiques indiquent que le flux de gènes interspécifique observé résulte d’introgressions anciennes (probablement au Pléistocène) et non contemporaines. Une dernière étude menée à l’échelle mondiale avec des marqueurs mitochondriaux a par ailleurs permis de montrer que les processus d’introduction de C. robusta diffèrent selon les régions d’introduction et pose la question du statut réellement non-indigène des deux espèces dans certaines régions. Ainsi, cette thèse a montré la (quasi)-absence d’hybridation actuelle entre C. robusta et C. intestinalis, en situation de syntopie. Elle ouvre des perspectives quant à l’étude des mécanismes d’isolement reproductif entre ces deux espèces. La question du devenir à long terme des deux espèces, qui par leur coexistence étroite sont en compétition, est posée. Cette compétition pourrait être modulée par leurs préférences environnementales et les changements climatiques en cours dans l’Atlantique Nord. Enfin, cette thèse illustre comment des processus contemporains et anciens interagissent pour façonner la distribution et l’évolution des espèces, la structure génétique de leurs populations et l’architecture de leur génome

Cryptic diversity and database errors challenge non-indigenous species surveys: An illustration with Botrylloides spp. in the English Channel and Mediterranean Sea

Molecular tools have been extensively used in recent decades to examine biological invasion processes, and are increasingly being adopted as efficient tools to support non-indigenous species surveys, notably through barcoding approaches, i.e., the use of a reference sequence specific to a given species to validate its identification. The technique is easy to use but requires reliable reference sequences to be available in public databases. In addition, the increasing discovery of cryptic species in marine taxa may complicate taxonomic assignment. We illustrate these two issues in the ascidian genus Botrylloides, in which at least three global marine invaders have been recognized, including B. violaceus and B. diegensis. We obtained COI sequences from >750 colonies of Botrylloides spp. sampled in W Europe or provided by expert colleagues from other regions. Phylogenetic trees clearly distinguished our targeted taxa [i.e., B. violaceus, B. diegensis and B. leachii (native)]. They also revealed another discrete lineage apparently related to a recently described eastern Mediterranean species. By examining public databases, we found sequences of B. diegensis erroneously assigned to B. leachii. This observation has major implications as the introduced B. diegensis can be misidentified as a putatively native species. We also checked published sequences of the genus Botrylloides in the Mediterranean Sea, complemented with new samples. Based on our custom reference database, all published sequences of B. leachii corresponded to B. diegensis, although this NIS has hardly been reported at all in the Mediterranean region. Such database errors are unfortunate, as the barcoding approach is a powerful tool to identify the recognized Botrylloides species currently present in European seas. This is of particular importance because a trait often used during field assessment, i.e., single-color vs. two-color colonies, is misleading to distinguish B. violaceus and B. diegensis respectively: a substantial proportion of the single-color morph are actually B. diegensis in both the Mediterranean Sea and the English Channel. Altogether, this study exemplifies the advantages and disadvantages of molecular barcoding in NIS surveys and studies. The limitations that were identified are all easy to resolve once proper vouchers and collections are set up

Isolation of 12 polymorphic tetranucleotide microsatellite markers of the leaf beetle Ophraella communa, a promising Ambrosia biocontrol agent also in Europe

Following its first record in Europe in 2013, the North American ragweed leaf beetle Ophraella communa, used already as a most successful biocontrol agent against common ragweed in China, is spreading rapidly, asking for a detailed analysis of the potential benefit and risk of this introduction for Europe. Here, we report twelve specific and polymorphic tetranucleotide microsatellite markers, which can be used for redrawing its global invasion history and spread across native and introduced ranges. The high level of polymorphism (i.e. from 4 to 18 alleles per locus) and the genetic variation detected within and between one native and two introduced populations provide adequate statistical power for elucidating the beetle’s invasion process

Contrasting global genetic patterns in two biologically similar, widespread and invasive Ciona species (Tunicata, Ascidiacea)

Human-mediated dispersal interplays with natural processes and complicates understanding of the biogeographical history of species. This is exemplified by two invasive tunicates, Ciona robusta (formerly Ciona intestinalis type A) and C. intestinalis (formerly Ciona intestinalis type B), globally distributed and sympatric in Europe. By gathering new mitochondrial sequences that were merged with published datasets, we analysed genetic patterns in different regions, with a focus on 1) their sympatric range and 2) allopatric populations in N and S America and southern Europe. In the sympatric range, the two species display contrasting genetic diversity patterns, with low polymorphism in C. robusta supporting the prevalent view of its recent introduction. In the E Pacific, several genetic traits support the non-native status of C. robusta. However, in the NE Pacific, this appraisal requires a complex scenario of introduction and should be further examined supported by extensive sampling efforts in the NW Pacific (putative native range). For C. intestinalis, Bayesian analysis suggested a natural amphi-North Atlantic distribution, casting doubt on its non-native status in the NW Atlantic. This study shows that both natural and human-mediated dispersal have influenced genetic patterns at broad scales; this interaction lessens our ability to confidently ascertain native vs. non-native status of populations, particularly of those species that are globally distributed

Comparative feeding rates of native and invasive ascidians

Ascidians have a recent history of species introductions globally, often with strong ecological impacts. Comparisons of per capita effects of invaders and comparable natives are useful to assess such impacts. Here, we explore ingestion rates (IR) and clearance rates (CR) of Ciona intestinalis and Ciona robusta, co-occurring native and non-native ascidians, respectively, from Brittany, France. IR was positively related to food concentration, with the invader responding more strongly to increasing food concentration. CR also differed by species, with the invader demonstrating higher values. C. robusta exhibited a higher functional response (Type I) than did C. intestinalis (Type II). Relative impact measured using seasonal abundance and IR revealed that C. robusta has a much greater impact than C. intestinalis at all food concentrations tested, though the former has a constrained distribution which limits its regional impact. Nevertheless, when abundant, we expect C. robusta to exert a greater impact on algal foods

Table S1: Characteristics of surveyed ships and hulls

Non-native ascidians are important members of the fouling community associated with artificial substrata and man-made structures. Being efficient fouling species, they are easily spread by human-mediated transports (e.g., with aquaculture trade and maritime transports). This is exemplified by the ascidian Asterocarpa humilis which displays a wide distribution in the Southern Hemisphere and has been recently reported in the Northern Hemisphere (NW Europe). In continental Chile, its first report dates back from 2000 for the locality of Antofagasta (23°S). Although there was no evidence about the vectors of introduction and spread, nor the source, some authors suggested maritime transport by ship hulls and aquaculture devices as putative introduction pathways and vectors. In the present study, we report for the first time the presence of A. humilis on the hull of an international ship in a commercial port in Concepción bay (36°S), south central Chile. We also found one individual associated to a seashell farm, 70 km far from Concepción bay. Further individuals were subsequently identified within Concepción bay: one juvenile settled upon international harbor pilings and a dozen individuals along aquaculture seashell longlines. For the first specimens sampled, species identification was ascertained using both morphological criteria and molecular barcoding, using the mitochondrial gene cytochrome c oxidase subunit I (COI) and a nuclear gene (ribosomal RNA 18S). The nuclear 18S gene and the mitochondrial gene COI clearly assigned the specimens to A. humilis, confirming our morphological identification. Two haplotypes were obtained with COI corresponding to haplotypes previously obtained with European and Northern Chilean specimens. The present study thus reports for the first time the presence of A. humilis in the Araucanian ecoregion, documenting the apparent expansion of this non-native tunicate in Chile over 2,000 km, spanning over three ecoregions. In addition we reveal the potential implication of the international maritime transport as a vector of spread of this species along the Eastern Pacific coast, and the putative role of aquaculture facilities in promoting local establishments of non-native tunicates

Eco-evolutive dynamic of two congeneric and interfertile ascidians, one native and one non-native, in their sympatric range

Les activités humaines sont à l’origine de profondes modifications de la distribution naturelle des espèces. Les introductions d’espèces sont en particulier à l’origine de contacts secondaires entre espèces non isolées reproductivement et ayant divergé en allopatrie. Cette situation est un cas d’étude particulièrement intéressant pour étudier des processus éco-évolutifs, tels que la coexistence d’espèces occupant de même niches écologiques ou les flux de gènes contemporains (i.e. hybridation et introgression) entre espèces indigènes et non-indigènes. Cette thèse s’est ainsi intéressée aux interactions écologiques et génomiques entre deux ascidies congénériques et interfertiles, Ciona robusta et Ciona intestinalis. Ces deux ascidies, abondantes dans les habitats portuaires, sont en sympatrie en Manche Occidentale suite à l’introduction récente de C. robusta (supposée originaire du Pacifique Nord-Ouest) dans l’aire de distribution naturelle de C. intestinalis. Par une étude de la distribution spatiale et temporelle (inter-saisonnière et inter- annuelle) des adultes des deux espèces et de la sédentarisation de leurs juvéniles, nous avons montré que les deux espèces coexistent de façon durable, au sein de communautés similaires, à l’échelle régionale. Elles vivent en syntopie dans la majorité des habitats portuaires étudiés, bien qu’il existe une importante dynamique saisonnière de leur abondance relative : C. robusta est surtout présente en fin d’été et en automne, et toujours en moindre abondance par rapport à sa congénère indigène. Cette syntopie, l’interfertilité des deux espèces et le synchronisme de leur maturité sexuelle indiquent un potentiel d’hybridation important entre les deux espèces. L’hybridation réalisée est pourtant faible, comme montré avec quatre marqueurs moléculaires diagnostiques des deux espèces, analysés sur plus de 3000 individus : seulement 4% des individus présentent des génotypes compatibles avec de l’hybridation ou de l’introgression. Ces résultats ont été complétés par une étude de génomique des populations (310 marqueurs SNPs et 450 individus collectés dans différents océans) : ils confirment que les flux de gènes interspécifiques sont très rares. Par ailleurs, les rares locus présentant du polymorphisme partagé montrent un taux d’introgression hétérogène, et l’introgression est également observée dans des localités où seule l’une des espèces existe (ex. côtes américaines et chiliennes). L’ensemble des résultats génétiques et génomiques indiquent que le flux de gènes interspécifique observé résulte d’introgressions anciennes (probablement au Pléistocène) et non contemporaines. Une dernière étude menée à l’échelle mondiale avec des marqueurs mitochondriaux a par ailleurs permis de montrer que les processus d’introduction de C. robusta diffèrent selon les régions d’introduction et pose la question du statut réellement non-indigène des deux espèces dans certaines régions. Ainsi, cette thèse a montré la (quasi)-absence d’hybridation actuelle entre C. robusta et C. intestinalis, en situation de syntopie. Elle ouvre des perspectives quant à l’étude des mécanismes d’isolement reproductif entre ces deux espèces. La question du devenir à long terme des deux espèces, qui par leur coexistence étroite sont en compétition, est posée. Cette compétition pourrait être modulée par leurs préférences environnementales et les changements climatiques en cours dans l’Atlantique Nord. Enfin, cette thèse illustre comment des processus contemporains et anciens interagissent pour façonner la distribution et l’évolution des espèces, la structure génétique de leurs populations et l’architecture de leur génome.Human activities severely alter species ranges that have been built on evolutionary time scales, and biological introductions promote secondary contacts between non-reproductively isolated species that were in allopatry. Such a situation is a very interesting case-study to examine eco-evolutionary processes, for instance coexistence between species sharing the same ecological niche or inter-specific gene flow (i.e. hybridization and introgression) between native and non-native species. This PhD thesis studied ecological and genomic interactions between two biologically similar, interfertile and congeneric tunicates, namely Ciona robusta and Ciona intestinalis. They are both abundant in harbours and marinas. They are sympatric in the Western English Channel because of the recent introduction of C. robusta (putatively native to Asia) in the natural range of C. intestinalis. Based on spatial and temporal (seasons and years) adult abundance data and examination of recruitment patterns of the two species, we showed that the two species are sustainably coexisting at a regional scale in Brittany, within similar communities. They live in syntopy in most of the study marinas. However, there are significant changes in their relative abundance through time: C. robusta is mostly present at the end of the summer and in the autumn, although always being less abundant than its native congener. Syntopy, interfertility between the two species and synchronous sexual maturity all indicated a high likelihood of hybridization between the two species. The realized hybridization is however very low, as shown by 4 species-diagnostic molecular markers genotyped over more than 3000 individuals: only 4% of the individuals displayed a genotype compatible with hybridization or introgression. This result has been confirmed with a population genomics study (310 SNPs; 450 individuals collected worldwide): inter-specific gene flow is very low. In addition, the few loci showing shared polymorphism displayed variable introgression rates and introgression was observed even in allopatric localities (where only one of the two species exists nowadays). Overall, the genetic and genomic results indicate that interspecific gene flow is most likely due to past introgression events (that may have occurred during the Pleistocene). Finally, a study carried out at a worldwide scale with two mitochondrial loci, showed that the introduction processes of C. robusta are different among the introduced regions. This study also questions the non-native status of the two Ciona species in some regions. This work showed the near absence of contemporary hybridization between C. robusta and C. intestinalis, even in syntopy, opening new research perspectives about the mechanisms preventing their reproduction in the wild. It also questions the fate of these two competing species; this competition may depend on the interaction between their specific environmental preferences and on on-going climatic changes in the North Atlantic. Altogether, this work illustrates the interplay between contemporary and past processes on species distribution and evolution, population genetic structure and genomic architecture

Sequences of haplotypes COX3-ND1 and concatenated mtDNA for Ciona robusta and Ciona intestinalis

Fasta sequences of COX3-ND1 and concatenated haplotypes (COI + COX3-ND1) for Ciona robusta and Ciona intestinali

Do settlement dynamics influence competitive interactions between an alien tunicate and its native congener?

International audienceVariation in density of early stages, that is, larvae and juveniles, is a major determinant of the distribution and abundance of the adult population of most marine invertebrates. These early stages thus play a key role in competitive interactions, and, more specifically, in invasion dynamics when biologically similar native and non-native species (NNS) come into contact in the same habitat. We examined the settlement dynamics and settlement rate of two important members of the fouling community that are common on human-made infrastructures around the world: Ciona robusta (formerly known as Ciona intestinalis type A) and C. intestinalis (formerly known as C. intestinalis type B). In the western English Channel, the two species live in close syntopy following the recent introduction of C. robusta in the native European range of C. intestinalis. Using settlement panels replaced monthly over 2 years in four marinas (including one studied over 4 years) and species-diagnostic molecular markers to distinguish between juveniles of both species (N = 1,650), we documented similar settlement dynamics of both species, with two settlement periods within a calendar year. With one exception, settlement times were highly similar in the congeners. Although the NNS showed lower settlement density than that of the native congener, its juvenile recruitment was high during the second settlement period that occurs after the warm season, a pattern also observed in adult populations. Altogether, our results suggest that species’ settlement dynamics do not lead to the dominance of one species over the other through space monopolization. In addition, we showed that changes over time are more pronounced in the NNS than in the native species. This is possibly due to a higher sensitivity of the NNS to changes of environmental factors such as temperature and salinity. Environmental changes may thus eventually modify the strength of competitive interactions between the two species as well as species dominance