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      Population genomics of the widespread African savannah trees Afzelia africana and Afzelia quanzensis reveals no significant past fragmentation of their distribution ranges

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          Most cited references58

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          Applications of next generation sequencing in molecular ecology of non-model organisms.

          As most biologists are probably aware, technological advances in molecular biology during the last few years have opened up possibilities to rapidly generate large-scale sequencing data from non-model organisms at a reasonable cost. In an era when virtually any study organism can 'go genomic', it is worthwhile to review how this may impact molecular ecology. The first studies to put the next generation sequencing (NGS) to the test in ecologically well-characterized species without previous genome information were published in 2007 and the beginning of 2008. Since then several studies have followed in their footsteps, and a large number are undoubtedly under way. This review focuses on how NGS has been, and can be, applied to ecological, population genetic and conservation genetic studies of non-model species, in which there is no (or very limited) genomic resources. Our aim is to draw attention to the various possibilities that are opening up using the new technologies, but we also highlight some of the pitfalls and drawbacks with these methods. We will try to provide a snapshot of the current state of the art for this rapidly advancing and expanding field of research and give some likely directions for future developments.
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            What can genetics tell us about population connectivity?

            Genetic data are often used to assess 'population connectivity' because it is difficult to measure dispersal directly at large spatial scales. Genetic connectivity, however, depends primarily on the absolute number of dispersers among populations, whereas demographic connectivity depends on the relative contributions to population growth rates of dispersal vs. local recruitment (i.e. survival and reproduction of residents). Although many questions are best answered with data on genetic connectivity, genetic data alone provide little information on demographic connectivity. The importance of demographic connectivity is clear when the elimination of immigration results in a shift from stable or positive population growth to negative population growth. Otherwise, the amount of dispersal required for demographic connectivity depends on the context (e.g. conservation or harvest management), and even high dispersal rates may not indicate demographic interdependence. Therefore, it is risky to infer the importance of demographic connectivity without information on local demographic rates and how those rates vary over time. Genetic methods can provide insight on demographic connectivity when combined with these local demographic rates, data on movement behaviour, or estimates of reproductive success of immigrants and residents. We also consider the strengths and limitations of genetic measures of connectivity and discuss three concepts of genetic connectivity that depend upon the evolutionary criteria of interest: inbreeding connectivity, drift connectivity, and adaptive connectivity. To conclude, we describe alternative approaches for assessing population connectivity, highlighting the value of combining genetic data with capture-mark-recapture methods or other direct measures of movement to elucidate the complex role of dispersal in natural populations.
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              New insights from fine-scale spatial genetic structure analyses in plant populations.

              Many empirical studies have assessed fine-scale spatial genetic structure (SGS), i.e. the nonrandom spatial distribution of genotypes, within plant populations using genetic markers and spatial autocorrelation techniques. These studies mostly provided qualitative descriptions of SGS, rendering quantitative comparisons among studies difficult. The theory of isolation by distance can predict the pattern of SGS under limited gene dispersal, suggesting new approaches, based on the relationship between pairwise relatedness coefficients and the spatial distance between individuals, to quantify SGS and infer gene dispersal parameters. Here we review the theory underlying such methods and discuss issues about their application to plant populations, such as the choice of the relatedness statistics, the sampling scheme to adopt, the procedure to test SGS, and the interpretation of spatial autocorrelograms. We propose to quantify SGS by an 'Sp' statistic primarily dependent upon the rate of decrease of pairwise kinship coefficients between individuals with the logarithm of the distance in two dimensions. Under certain conditions, this statistic estimates the reciprocal of the neighbourhood size. Reanalysing data from, mostly, published studies, the Sp statistic was assessed for 47 plant species. It was found to be significantly related to the mating system (higher in selfing species) and to the life form (higher in herbs than trees), as well as to the population density (higher under low density). We discuss the necessity for comparing SGS with direct estimates of gene dispersal distances, and show how the approach presented can be extended to assess (i) the level of biparental inbreeding, and (ii) the kurtosis of the gene dispersal distribution.
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                Author and article information

                Journal
                American Journal of Botany
                Am J Bot
                Wiley
                0002-9122
                1537-2197
                March 2020
                March 22 2020
                March 2020
                : 107
                : 3
                : 498-509
                Affiliations
                [1 ]Forest is Life, TERRA Teaching and Research Centre Gembloux Agro‐Bio TechUniversity of Liège 2 Passage des DéportésB‐5030Gembloux Belgium
                [2 ]Evolutionary Biology and Ecology Unit, CP 160/12 Faculté des Sciences Université Libre de Bruxelles 50 avenue F. D. RooseveltB‐1050Brussels Belgium
                [3 ]Univ. BordeauxINRAEBFP 71 Avenue Edouard BourlauxF‐33882Villenave d'Ornon France
                [4 ]University of Exeter, GeographyCollege of Life and Environmental Sciences Stocker roadEX44QDExeter UK
                [5 ]Evolutionary Genomics Centre for Geogenetics ‐ Natural History Museum of Denmark Øster Voldgade 5‐71350Copenhagen K Denmark
                [6 ]Univ. BordeauxINRAEBIOGECO 69 route d'ArcachonF‐33610Cestas France
                [7 ]DIADE, IRD University of Montpellier 911 Avenue Agropolis, BP 6450134394Montpellier France
                [8 ]Bioversity International, Forest Genetic Resources and Restoration Programme Sub‐Regional Office for Central Africa P.O. Box 2008, Messa Yaoundé Cameroon
                [9 ]Université d'Agriculture de Kétou BP: 43Kétou Benin
                Article
                10.1002/ajb2.1449
                6ad44b94-91e6-4767-9af1-5803827636c3
                © 2020

                http://onlinelibrary.wiley.com/termsAndConditions#vor

                http://doi.wiley.com/10.1002/tdm_license_1.1

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