Longitudinal trends in climate drive flowering time clines in North American Arabidopsis thaliana

Introduced species frequently show geographic differentiation, and when differentiation mirrors the ancestral range, it is often taken as evidence of adaptive evolution. The mouse-ear cress (Arabidopsis thaliana) was introduced to North America from Eurasia 150-200 years ago, providing an opportunity to study parallel adaptation in a genetic model organism. Here, we test for clinal variation in flowering time using 199 North American (NA) accessions of A. thaliana, and evaluate the contributions of major flowering time genes FRI, FLC, and PHYC as well as potential ecological mechanisms underlying differentiation. We find evidence for substantial within population genetic variation in quantitative traits and flowering time, and putatively adaptive longitudinal differentiation, despite low levels of variation at FRI, FLC, and PHYC and genome-wide reductions in population structure relative to Eurasian (EA) samples. The observed longitudinal cline in flowering time in North America is parallel to an EA cline, robust to the effects of population structure, and associated with geographic variation in winter precipitation and temperature. We detected major effects of FRI on quantitative traits associated with reproductive fitness, although the haplotype associated with higher fitness remains rare in North America. Collectively, our results suggest the evolution of parallel flowering time clines through novel genetic mechanisms.     

Dispersal in the course of an invasion

Invasive species receive attention as manifestations of global ecological change and because of the effects that they may have on other organisms. They are commonly discussed in the context of the ecological perturbations or the human activities that permitted the invasion. There is also evidence, that there is an intrinsic component to biological invasions in that evolutionary changes of the invaders themselves can facilitate or limit invasions (Lee 2002; Urban et al. 2007; Van Bocxlaer et al. 2010). Hence, teasing apart whether environmental change or changes of the organism foster invasions is an interesting field of research. Ample evidence for plants and animals documents that ecological change and human activities trigger range expansions and invasions, but questions regarding evolutionary change of invaders remain less explored although there are several reasons to believe it matters. Firstly, rapid evolutionary change is possible in time-frames relevant for contemporary biological invasions(Hendry et al. 2007). Furthermore, population genetic modelling suggests that there are circumstances where the range expansion and colonization of empty spaces in the course of an invasion can induce evolutionary change in a way that is specific to invaders: the process of repeated founding out of marginal populations in the course of a range expansion can shift allele frequencies and has been referred to as allele surfing, which not only affects neutral genetic variance, but also fitness relevant traits (Klopfstein et al. 2006; Travis et al. 2007; Burton & Travis 2008). Importantly, this process poses a null model for evolutionary inference in invasive populations. It predicts conspicuous allele frequency changes in an expanding metapopulation unless migration homogenizes the gene pool. Despite this relevance, ideas about allele surfing rely heavily on modelling although some experimental evidence comes from studies that document the segregation of genetic variants in growing plaques of bacteria (Hallatschek et al. 2007). To date, little empirical data is available that would reveal the migration processes that affect the establishment of gene pools at invasion fronts in natural systems. This aspect sets the study of Bronnenhuber et al. (2011) apart. They quantify migration behind the expansion front of an invading fish and thus provide important baseline data for the interpretation of the emerging patterns of genetic differentiation.     

The cane toad's (Chaunus [Bufo] marinus) increasing ability to invade Australia is revealed by a dynamically updated range model

Invasive species threaten biological diversity throughout the world. Understanding the dynamics of their spread is critical to mitigating this threat. In Australia, efforts are underway to control the invasive cane toad (Chaunus [Bufo] marinus). Range models based on their native bioclimatic envelope suggest that the cane toad is nearing the end of its invasion phase. However, such models assume a conserved niche between native and invaded regions and the absence of evolution to novel habitats. Here, we develop a dynamically updated statistical model to predict the growing extent of cane toad range based on their current distribution in Australia. Results demonstrate that Australian cane toads may already have the ability to spread across an area that almost doubles their current range and that triples projections based on their native distribution. Most of the expansion in suitable habitat area has occurred in the last decade and in regions characterized by high temperatures. Increasing use of extreme habitats may indicate that novel ecological conditions have facilitated a broader realized niche or that toad populations at the invasion front have evolved greater tolerance to extreme abiotic conditions. Rapid evolution to novel habitats combined with ecological release from native enemies may explain why some species become highly successful global invaders. Predicting species ranges following invasion or climate change may often require dynamically updated range models that incorporate a broader realization of niches in the absence of natural enemies and evolution in response to novel habitats.     

基因组学: 理解植物入侵性的重要工具

入侵植物基因组学是一个新兴的研究领域, 它利用基因组学方法研究与植物入侵性相关的分子基础和表达调控机制, 甄别入侵性基因型, 进而在基因组水平上揭示外来种入侵性产生和进化的分子机制。本文扼要综述了可用于植物入侵生物学研究的主要基因组学方法, 包括比较基因组学、群体基因组学和表观基因组学等方法; 运用基因组学技术研究入侵植物除草剂抗性和根状茎发育的分子基础已取得了重要进展。然而, 入侵植物基因组学仍处于发展初期, 选择理想的入侵植物模式种, 建立入侵性研究的模式系统, 是当前亟待解决的问题。本文还提出了入侵植物基因组学研究值得关注的几个发展方向, 包括基因组信息的完善、不同环境条件下入侵植物的分子响应机制以及入侵性的系统生物学研究等。     

The evolutionary consequences of biological invasions

A major challenge of invasion biology is the development of a predictive framework that prevents new invasions. This is inherently difficult because different biological characteristics are important at the different stages of invasion: opportunity/transport, establishment and spread. Here, we draw from recent research on a variety of taxa to examine the evolutionary causes and consequences of biological invasions. The process of introduction may favour species with characteristics that promote success in highly disturbed, human-dominated landscapes, thus exerting novel forms of selection on introduced populations. Moreover, evidence is accumulating that multiple introductions can often be critical to the successful establishment and spread of introduced species, as they may be important sources of genetic variation necessary for adaptation in new environments or may permit the introduction of novel traits. Thus, not only should the introduction of new species be prevented, but substantial effort should also be directed to preventing the secondary introduction of previously established species (and even movement of individuals among introduced populations). Modern molecular techniques can take advantage of genetic changes postintroduction to determine the source of introduced populations and their vectors of spread, and to elucidate the mechanisms of success of some invasive species. Moreover, the growing availability of genomic tools will permit the identification of underlying genetic causes of invasive success.     

Assessing the speed and predictability of local adaptation in invasive California poppies (Eschscholzia californica)

Insight into the speed and predictability of local adaptation can be gained by studying organisms, such as invasive species, that have recently expanded their geographical ranges. Common garden studies were designed to address these issues with the California poppy, Eschscholzia californica, collected from a wide range of environments in both its native (California) and invasive (Chile) ranges. We found similar patterns of plant trait variation along similar abiotic gradients in plants collected from both areas. Multivariate analysis demonstrated that coastal plants from both areas tended to be shorter, smaller plants with smaller seeds and flowers that germinate and flower later than plants collected from inland locations. In addition, size and fecundity traits in both native and invasive poppies were correlated with average rainfall totals; the plants that grew the largest and were the most fecund during the first year of growth originated from the driest areas. This parallel variation suggests that these traits are adaptive and that these patterns have evolved in Chile during the 110-150 years since introduction.