实验进化与植物学研究相关吗?

IF 2.4 2区 生物学 Q2 PLANT SCIENCES American Journal of Botany Pub Date : 2024-02-21 DOI:10.1002/ajb2.16296
Florian P. Schiestl
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Therefore, single-generation studies, that merely capture a single frame out of the “evolutionary footage”, may fall short of documenting the evolutionary dimension, which is one of relentless change. For example, in community ecology experiments lasting for several plant generations, drift and selection may have changed the (epi)genotypic composition of the experimental populations, hence having an effect of the outcomes and repeatability of the experiment (van Moorsel et al., <span>2019</span>). When studying floral traits including rates of selfing, one should be aware that they may evolve rapidly when pollinator communities change (Gervasi and Schiestl, <span>2017</span>). Lastly, for decisions to be made in terms of how threatened plant populations can be conserved, their potential to adapt to changing environmental parameters may be a key consideration (Jump and Penuelas, <span>2005</span>). I argue that we should more often consider the opportunity for addressing real-time evolution in our research, by including an evolutionary framework in our experimental design, and build in the evolutionary dimension in ecological- and plant conservation models.</p><p>There are different ways to study real-time evolution directly or by incorporating it into experiments with another primary focus. Perhaps the most commonly used way is to use comparative approaches between populations or long-term studies without manipulating environmental parameters. Resurrection experiments, done by growing stored “historical” seeds together with the recent ones (Franks et al., <span>2016</span>) or comparing genomes of herbarium samples with those of recent populations (Kreiner et al., <span>2022</span>), provide additional approaches for assessing intermediate- to short-term evolutionary changes. Experimental evolution, defined as “the study of evolutionary changes occurring in experimental populations as a consequence of conditions (environmental, demographic, genetic, social, and so forth) imposed by the experimenter” (Kawecki et al., <span>2012</span>) strives to identify “natural” evolution by using realistic ecological factors (as opposed to studies with artificial selection), in natural, or semi-natural greenhouse-based conditions. The advantage of this approach is that it usually allows one to identify the causative factors for evolutionary change.</p><p>Whereas experimental evolution has proven highly successful, it has mostly focused on microbes and animals, especially insects, whereas plants have rarely been the focus of this research avenue (Kawecki et al., <span>2012</span>). This matters for botany because results obtained with microbes and animals cannot easily be extrapolated to plants, because plants, with their autotroph feeding, sessile lifestyle, and unique pollination- and mating systems, evolve under different kinds of selection and face different constraints and trade-offs than those of mobile, heterotroph organisms, or those with more simple phenotypes like microbes. Long-term experiments with plants have mostly focused on aspects of plant community change with environmental parameters, and evolutionary questions therein being more a research side-line (van Moorsel et al., <span>2019</span>). Only a handful of studies, however, have performed experiments that specifically targeted “real-time” evolution in plants (see Appendix S1).</p><p>Most likely, the scarcity of experimental evolution studies in plants is due to their comparatively long generation time, making evolution experiments last comparatively long, even when experiments run for only few generations.</p><p>Despite this challenge, plants provide powerful models for evolutionary experiments, because they are easier to work with than their animal counterparts in several aspects. For example, the lack of mobility in plants allows for an easy assessment of fitness components (e.g., seed set or survival) and enables the setup of experimental plots in the field for trans-generational research (Agrawal et al., <span>2012</span>). The presence of seeds in spermatophytes or spores in ferns and mosses makes it possible to store a population of individuals, often for many decades, to use them as a backup of intermediate generations during an experiment, or for resurrection experiments towards the end of the experiment. Plants also have great variability in mating systems, impacting parameters of population genetics as well as the practicability of an experiment. In obligatory selfers such as <i>Arabidopsis thaliana</i> (L.) Heynh. [Brassicaceae], no pollen vector is needed, but there is also no effective sexual recombination, hence the response to selection is a sorting of genotypes among the ones initially present in the starting population of the experiment, making it easier to quantify genotypic changes across generations (Züst et al., <span>2012</span>). Outcrossing plants, in contrast, need pollen vectors for sexual reproduction, and have effective sexual recombination, higher heterozygosity, less linkage disequilibrium and potentially higher adaptability (Lucek and Willi, <span>2021</span>). Because animal pollinators as well as abiotic pollen vectors such as wind are strong selective factors in plants (Gervasi and Schiestl, <span>2017</span>; Tonnabel et al., <span>2022</span>), this additional layer of selection makes evolution experiments with outcrossing plants fascinating, yet more challenging in their setup. Naturally, variation in pollination and mating system is also a fascinating research topic that has recently successfully been approached with real-time evolution experiments, showing for example, rapid evolution of selfing and sex allocation (Dorken and Pannell, <span>2009</span>; Roels and Kelly, <span>2011</span>), as well as divergent evolution after pollinator switch (Figure 1; Gervasi and Schiestl, <span>2017</span>). In botany, there is wide scope for studying genes, genomes, traits, species, interactions, and even ecosystems in the view of rapid evolution. How plants adapt to environmental parameters, and how trade-offs, constraints, or pleiotropy impact this process is of interest for both basic and more applied research. Importantly, current environmental change is pertinent due to warming climate, intensified agriculture, deforesting, increased fragmentation, declining pollinators, etc. It is safe to assume that all these parameters will impact natural selection and thus adaptive evolution in nature. Therefore, it is timely to address adaptive evolution experimentally, and develop appropriate models for predicting its outcome. Such experiments can be set up in a greenhouse, allowing for great control of environmental factors, and thus great power of recognizing causative factors in evolution. Alternatively, plots can be set up in experimental fields, providing a superior natural setting, yet less easy identification of specific factors causing evolutionary change. A key question for any experimental approach is whether evolution in an artificial or manipulated ecosystem, either in the greenhouse or in the field, effectively mimics evolution in natural ecosystems.</p><p>A particularly timely example for the need to address evolutionary questions is the science of plant conservation (Olivieri et al., <span>2016</span>). Models of adaptability are deeply desired in conservation biology, to predict which populations of rare plants will be able to adapt, and which need measures like assisted migration for survival (Jump and Penuelas, <span>2005</span>). Rapid adaptation is also of concern in invasive species, that may threaten rare natives (Alexander, <span>2013</span>). Experimental evolution can act as a kind of test for adaptability or evolutionary rescue (Gonzalez et al., <span>2013</span>), as done in alpine species of <i>Drosophila</i>, showing a lack of ability to adapt to warmer temperatures (Kinzner et al., <span>2019</span>). This approach is even more powerful when combined with genomics, in an “evolve and re-sequence” approach. In evolve and re-sequence experiments, the adaptive potential of experimental populations is tested in response to specific factors such as temperature change or drought. Subsequently, plant populations before and after evolution are genotyped and changes in frequencies of specific alleles can be assessed. Such tests of adaptability and assessment of adaptive genetic variation can yield powerful models of variation in specific genes that enable adaptation. This approach has been used in <i>Drosophila</i> to establish that adaptability to harsh environments is correlated to genome-wide variability, rather than patterns of inbreeding (Orsted et al., <span>2019</span>). Similarly, Stelkens et al. (<span>2014</span>) showed in yeast that hybridization enables evolutionary rescue and adaptation to degraded environments.</p><p>Real-time evolution in botany may gain more momentum in the future by the development of new fast-cycling model plant species, analogous to the rapid cycling <i>Brassica</i> [Brassicaceae] species bred by Paul Williams a few decades ago. This would also help to address a greater variety of research questions in a real-time evolution context, because a few “model” species are not enough to represent the diversity of biological functions found in plants. Developing new fast-cycling models would, for example, require artificially selecting for short generation time in an annual plant, yet maintaining genome-wide genetic variability, to allow for sufficient adaptability in subsequent experiments. Besides having an annual life cycle, such plants should be easy to grow, have seeds that can be stored for long time periods, and with easy subsequent germination. Annual species of <i>Mimulus</i> [Phrymaceae], <i>Consolida</i> [Ranunculaceae], <i>Aquilegia</i> [Ranunculaceae], <i>Plantago</i> [Plantaginaceae], <i>Helianthus</i> [Asteraceae], and several members of the Brassicaceae and the Poaceae may be good candidates for such new models, to name just a few. Plants adapted to habitats with naturally short vegetation period, such as desert or alpine annuals, may be promising, too. Selecting for shorter generation time in any plant species may be an interesting experiment in itself, allowing quantitative genetic studies of generation time and its pleiotropic effects. New fast-cycling models would reveal fascinating opportunities for new studies that include the evolutionary dimension, something highly desirable for future botanical research.</p>","PeriodicalId":7691,"journal":{"name":"American Journal of Botany","volume":null,"pages":null},"PeriodicalIF":2.4000,"publicationDate":"2024-02-21","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://onlinelibrary.wiley.com/doi/epdf/10.1002/ajb2.16296","citationCount":"0","resultStr":"{\"title\":\"Is experimental evolution relevant for botanical research?\",\"authors\":\"Florian P. Schiestl\",\"doi\":\"10.1002/ajb2.16296\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p>Most researchers in botany acknowledge the importance of evolution in shaping plant traits, communities, or interactions with other organisms, but nevertheless implicitly assume that ongoing evolutionary change is not fast enough to impact the outcome or repeatability of their research. Although this may be true for some studies, especially those focusing on macroevolution, for others it is less clear, because more and more research shows that evolution can be rapid in some cases, especially when selection is strong and the generation time of the evolving organisms is short (Agrawal et al., <span>2012</span>; Franks et al., <span>2016</span>; Ramos and Schiestl, <span>2019</span>). Therefore, single-generation studies, that merely capture a single frame out of the “evolutionary footage”, may fall short of documenting the evolutionary dimension, which is one of relentless change. For example, in community ecology experiments lasting for several plant generations, drift and selection may have changed the (epi)genotypic composition of the experimental populations, hence having an effect of the outcomes and repeatability of the experiment (van Moorsel et al., <span>2019</span>). When studying floral traits including rates of selfing, one should be aware that they may evolve rapidly when pollinator communities change (Gervasi and Schiestl, <span>2017</span>). Lastly, for decisions to be made in terms of how threatened plant populations can be conserved, their potential to adapt to changing environmental parameters may be a key consideration (Jump and Penuelas, <span>2005</span>). I argue that we should more often consider the opportunity for addressing real-time evolution in our research, by including an evolutionary framework in our experimental design, and build in the evolutionary dimension in ecological- and plant conservation models.</p><p>There are different ways to study real-time evolution directly or by incorporating it into experiments with another primary focus. Perhaps the most commonly used way is to use comparative approaches between populations or long-term studies without manipulating environmental parameters. Resurrection experiments, done by growing stored “historical” seeds together with the recent ones (Franks et al., <span>2016</span>) or comparing genomes of herbarium samples with those of recent populations (Kreiner et al., <span>2022</span>), provide additional approaches for assessing intermediate- to short-term evolutionary changes. Experimental evolution, defined as “the study of evolutionary changes occurring in experimental populations as a consequence of conditions (environmental, demographic, genetic, social, and so forth) imposed by the experimenter” (Kawecki et al., <span>2012</span>) strives to identify “natural” evolution by using realistic ecological factors (as opposed to studies with artificial selection), in natural, or semi-natural greenhouse-based conditions. The advantage of this approach is that it usually allows one to identify the causative factors for evolutionary change.</p><p>Whereas experimental evolution has proven highly successful, it has mostly focused on microbes and animals, especially insects, whereas plants have rarely been the focus of this research avenue (Kawecki et al., <span>2012</span>). This matters for botany because results obtained with microbes and animals cannot easily be extrapolated to plants, because plants, with their autotroph feeding, sessile lifestyle, and unique pollination- and mating systems, evolve under different kinds of selection and face different constraints and trade-offs than those of mobile, heterotroph organisms, or those with more simple phenotypes like microbes. Long-term experiments with plants have mostly focused on aspects of plant community change with environmental parameters, and evolutionary questions therein being more a research side-line (van Moorsel et al., <span>2019</span>). Only a handful of studies, however, have performed experiments that specifically targeted “real-time” evolution in plants (see Appendix S1).</p><p>Most likely, the scarcity of experimental evolution studies in plants is due to their comparatively long generation time, making evolution experiments last comparatively long, even when experiments run for only few generations.</p><p>Despite this challenge, plants provide powerful models for evolutionary experiments, because they are easier to work with than their animal counterparts in several aspects. For example, the lack of mobility in plants allows for an easy assessment of fitness components (e.g., seed set or survival) and enables the setup of experimental plots in the field for trans-generational research (Agrawal et al., <span>2012</span>). The presence of seeds in spermatophytes or spores in ferns and mosses makes it possible to store a population of individuals, often for many decades, to use them as a backup of intermediate generations during an experiment, or for resurrection experiments towards the end of the experiment. Plants also have great variability in mating systems, impacting parameters of population genetics as well as the practicability of an experiment. In obligatory selfers such as <i>Arabidopsis thaliana</i> (L.) Heynh. [Brassicaceae], no pollen vector is needed, but there is also no effective sexual recombination, hence the response to selection is a sorting of genotypes among the ones initially present in the starting population of the experiment, making it easier to quantify genotypic changes across generations (Züst et al., <span>2012</span>). Outcrossing plants, in contrast, need pollen vectors for sexual reproduction, and have effective sexual recombination, higher heterozygosity, less linkage disequilibrium and potentially higher adaptability (Lucek and Willi, <span>2021</span>). Because animal pollinators as well as abiotic pollen vectors such as wind are strong selective factors in plants (Gervasi and Schiestl, <span>2017</span>; Tonnabel et al., <span>2022</span>), this additional layer of selection makes evolution experiments with outcrossing plants fascinating, yet more challenging in their setup. Naturally, variation in pollination and mating system is also a fascinating research topic that has recently successfully been approached with real-time evolution experiments, showing for example, rapid evolution of selfing and sex allocation (Dorken and Pannell, <span>2009</span>; Roels and Kelly, <span>2011</span>), as well as divergent evolution after pollinator switch (Figure 1; Gervasi and Schiestl, <span>2017</span>). In botany, there is wide scope for studying genes, genomes, traits, species, interactions, and even ecosystems in the view of rapid evolution. How plants adapt to environmental parameters, and how trade-offs, constraints, or pleiotropy impact this process is of interest for both basic and more applied research. Importantly, current environmental change is pertinent due to warming climate, intensified agriculture, deforesting, increased fragmentation, declining pollinators, etc. It is safe to assume that all these parameters will impact natural selection and thus adaptive evolution in nature. Therefore, it is timely to address adaptive evolution experimentally, and develop appropriate models for predicting its outcome. Such experiments can be set up in a greenhouse, allowing for great control of environmental factors, and thus great power of recognizing causative factors in evolution. Alternatively, plots can be set up in experimental fields, providing a superior natural setting, yet less easy identification of specific factors causing evolutionary change. A key question for any experimental approach is whether evolution in an artificial or manipulated ecosystem, either in the greenhouse or in the field, effectively mimics evolution in natural ecosystems.</p><p>A particularly timely example for the need to address evolutionary questions is the science of plant conservation (Olivieri et al., <span>2016</span>). Models of adaptability are deeply desired in conservation biology, to predict which populations of rare plants will be able to adapt, and which need measures like assisted migration for survival (Jump and Penuelas, <span>2005</span>). Rapid adaptation is also of concern in invasive species, that may threaten rare natives (Alexander, <span>2013</span>). Experimental evolution can act as a kind of test for adaptability or evolutionary rescue (Gonzalez et al., <span>2013</span>), as done in alpine species of <i>Drosophila</i>, showing a lack of ability to adapt to warmer temperatures (Kinzner et al., <span>2019</span>). This approach is even more powerful when combined with genomics, in an “evolve and re-sequence” approach. In evolve and re-sequence experiments, the adaptive potential of experimental populations is tested in response to specific factors such as temperature change or drought. Subsequently, plant populations before and after evolution are genotyped and changes in frequencies of specific alleles can be assessed. Such tests of adaptability and assessment of adaptive genetic variation can yield powerful models of variation in specific genes that enable adaptation. This approach has been used in <i>Drosophila</i> to establish that adaptability to harsh environments is correlated to genome-wide variability, rather than patterns of inbreeding (Orsted et al., <span>2019</span>). Similarly, Stelkens et al. (<span>2014</span>) showed in yeast that hybridization enables evolutionary rescue and adaptation to degraded environments.</p><p>Real-time evolution in botany may gain more momentum in the future by the development of new fast-cycling model plant species, analogous to the rapid cycling <i>Brassica</i> [Brassicaceae] species bred by Paul Williams a few decades ago. This would also help to address a greater variety of research questions in a real-time evolution context, because a few “model” species are not enough to represent the diversity of biological functions found in plants. Developing new fast-cycling models would, for example, require artificially selecting for short generation time in an annual plant, yet maintaining genome-wide genetic variability, to allow for sufficient adaptability in subsequent experiments. Besides having an annual life cycle, such plants should be easy to grow, have seeds that can be stored for long time periods, and with easy subsequent germination. Annual species of <i>Mimulus</i> [Phrymaceae], <i>Consolida</i> [Ranunculaceae], <i>Aquilegia</i> [Ranunculaceae], <i>Plantago</i> [Plantaginaceae], <i>Helianthus</i> [Asteraceae], and several members of the Brassicaceae and the Poaceae may be good candidates for such new models, to name just a few. Plants adapted to habitats with naturally short vegetation period, such as desert or alpine annuals, may be promising, too. Selecting for shorter generation time in any plant species may be an interesting experiment in itself, allowing quantitative genetic studies of generation time and its pleiotropic effects. 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引用次数: 0

摘要

植物的交配系统也有很大的差异,这影响到群体遗传学的参数以及实验的可行性。在拟南芥(Arabidopsis thaliana (L.) Heynh.拟南芥[十字花科]不需要花粉载体,但也不存在有效的有性重组,因此对选择的反应是在实验起始群体中最初存在的基因型之间进行排序,从而更容易量化跨代的基因型变化(Züst 等人,2012 年)。相比之下,外交植物需要花粉载体进行有性生殖,具有有效的有性重组、较高的杂合度、较少的连锁不平衡以及潜在的较高适应性(Lucek 和 Willi,2021 年)。由于动物授粉者以及风等非生物花粉载体是植物的强选择性因素(Gervasi 和 Schiestl,2017 年;Tonnabel 等人,2022 年),这一额外的选择层使得外交植物的进化实验非常吸引人,但其设置更具挑战性。自然,授粉和交配系统的变异也是一个引人入胜的研究课题,最近已成功地通过实时进化实验进行了研究,例如显示了自交和性别分配的快速进化(Dorken 和 Pannell,2009 年;Roels 和 Kelly,2011 年),以及授粉者转换后的分化进化(图 1;Gervasi 和 Schiestl,2017 年)。在植物学中,从快速进化的角度研究基因、基因组、性状、物种、相互作用甚至生态系统都有广阔的空间。植物如何适应环境参数,以及权衡、限制或多效性如何影响这一过程,是基础研究和应用研究的兴趣所在。重要的是,当前的环境变化与气候变暖、农业集约化、森林砍伐、破碎化加剧、传粉昆虫减少等有关。可以肯定的是,所有这些参数都会影响自然选择,从而影响自然界的适应性进化。因此,通过实验解决适应性进化问题,并建立预测其结果的适当模型,是非常及时的。这种实验可以在温室中进行,这样可以很好地控制环境因素,从而很好地识别进化中的致因。或者,也可以在实验田里建立实验点,提供优越的自然环境,但不太容易识别引起进化变化的具体因素。任何实验方法的一个关键问题是,在温室或田野中,人工或受操纵生态系统中的进化是否能有效模拟自然生态系统中的进化。在保护生物学中,人们非常需要适应性模型,以预测哪些稀有植物种群能够适应环境,哪些种群需要辅助迁移等措施才能生存(Jump 和 Penuelas,2005 年)。入侵物种的快速适应性也令人担忧,因为它可能会威胁到稀有的本地物种(Alexander,2013 年)。实验进化可以作为一种适应性或进化拯救的测试(Gonzalez 等人,2013 年),就像在果蝇的高山物种中所做的那样,实验表明果蝇缺乏适应较高温度的能力(Kinzner 等人,2019 年)。这种方法如果与基因组学相结合,采用 "进化和重测序 "的方法,效果会更加显著。在 "进化与重排序列 "实验中,实验种群的适应潜力将针对温度变化或干旱等特定因素进行测试。随后,对进化前后的植物种群进行基因分型,评估特定等位基因频率的变化。这种对适应性的测试和对适应性遗传变异的评估可以产生强大的特定基因变异模型,从而实现适应性。这种方法已被用于果蝇,以确定对恶劣环境的适应性与全基因组变异相关,而非近交模式(Orsted 等人,2019 年)。同样,Stelkens 等人(2014 年)在酵母中发现,杂交可以实现进化拯救和适应退化环境。未来,通过开发新的快速循环模式植物物种,植物学的实时进化可能会获得更大的动力,类似于几十年前保罗-威廉姆斯培育的快速循环芸薹属[十字花科]物种。这也将有助于在实时进化的背景下解决更多的研究问题,因为几个 "模式 "物种不足以代表植物生物功能的多样性。
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Is experimental evolution relevant for botanical research?

Most researchers in botany acknowledge the importance of evolution in shaping plant traits, communities, or interactions with other organisms, but nevertheless implicitly assume that ongoing evolutionary change is not fast enough to impact the outcome or repeatability of their research. Although this may be true for some studies, especially those focusing on macroevolution, for others it is less clear, because more and more research shows that evolution can be rapid in some cases, especially when selection is strong and the generation time of the evolving organisms is short (Agrawal et al., 2012; Franks et al., 2016; Ramos and Schiestl, 2019). Therefore, single-generation studies, that merely capture a single frame out of the “evolutionary footage”, may fall short of documenting the evolutionary dimension, which is one of relentless change. For example, in community ecology experiments lasting for several plant generations, drift and selection may have changed the (epi)genotypic composition of the experimental populations, hence having an effect of the outcomes and repeatability of the experiment (van Moorsel et al., 2019). When studying floral traits including rates of selfing, one should be aware that they may evolve rapidly when pollinator communities change (Gervasi and Schiestl, 2017). Lastly, for decisions to be made in terms of how threatened plant populations can be conserved, their potential to adapt to changing environmental parameters may be a key consideration (Jump and Penuelas, 2005). I argue that we should more often consider the opportunity for addressing real-time evolution in our research, by including an evolutionary framework in our experimental design, and build in the evolutionary dimension in ecological- and plant conservation models.

There are different ways to study real-time evolution directly or by incorporating it into experiments with another primary focus. Perhaps the most commonly used way is to use comparative approaches between populations or long-term studies without manipulating environmental parameters. Resurrection experiments, done by growing stored “historical” seeds together with the recent ones (Franks et al., 2016) or comparing genomes of herbarium samples with those of recent populations (Kreiner et al., 2022), provide additional approaches for assessing intermediate- to short-term evolutionary changes. Experimental evolution, defined as “the study of evolutionary changes occurring in experimental populations as a consequence of conditions (environmental, demographic, genetic, social, and so forth) imposed by the experimenter” (Kawecki et al., 2012) strives to identify “natural” evolution by using realistic ecological factors (as opposed to studies with artificial selection), in natural, or semi-natural greenhouse-based conditions. The advantage of this approach is that it usually allows one to identify the causative factors for evolutionary change.

Whereas experimental evolution has proven highly successful, it has mostly focused on microbes and animals, especially insects, whereas plants have rarely been the focus of this research avenue (Kawecki et al., 2012). This matters for botany because results obtained with microbes and animals cannot easily be extrapolated to plants, because plants, with their autotroph feeding, sessile lifestyle, and unique pollination- and mating systems, evolve under different kinds of selection and face different constraints and trade-offs than those of mobile, heterotroph organisms, or those with more simple phenotypes like microbes. Long-term experiments with plants have mostly focused on aspects of plant community change with environmental parameters, and evolutionary questions therein being more a research side-line (van Moorsel et al., 2019). Only a handful of studies, however, have performed experiments that specifically targeted “real-time” evolution in plants (see Appendix S1).

Most likely, the scarcity of experimental evolution studies in plants is due to their comparatively long generation time, making evolution experiments last comparatively long, even when experiments run for only few generations.

Despite this challenge, plants provide powerful models for evolutionary experiments, because they are easier to work with than their animal counterparts in several aspects. For example, the lack of mobility in plants allows for an easy assessment of fitness components (e.g., seed set or survival) and enables the setup of experimental plots in the field for trans-generational research (Agrawal et al., 2012). The presence of seeds in spermatophytes or spores in ferns and mosses makes it possible to store a population of individuals, often for many decades, to use them as a backup of intermediate generations during an experiment, or for resurrection experiments towards the end of the experiment. Plants also have great variability in mating systems, impacting parameters of population genetics as well as the practicability of an experiment. In obligatory selfers such as Arabidopsis thaliana (L.) Heynh. [Brassicaceae], no pollen vector is needed, but there is also no effective sexual recombination, hence the response to selection is a sorting of genotypes among the ones initially present in the starting population of the experiment, making it easier to quantify genotypic changes across generations (Züst et al., 2012). Outcrossing plants, in contrast, need pollen vectors for sexual reproduction, and have effective sexual recombination, higher heterozygosity, less linkage disequilibrium and potentially higher adaptability (Lucek and Willi, 2021). Because animal pollinators as well as abiotic pollen vectors such as wind are strong selective factors in plants (Gervasi and Schiestl, 2017; Tonnabel et al., 2022), this additional layer of selection makes evolution experiments with outcrossing plants fascinating, yet more challenging in their setup. Naturally, variation in pollination and mating system is also a fascinating research topic that has recently successfully been approached with real-time evolution experiments, showing for example, rapid evolution of selfing and sex allocation (Dorken and Pannell, 2009; Roels and Kelly, 2011), as well as divergent evolution after pollinator switch (Figure 1; Gervasi and Schiestl, 2017). In botany, there is wide scope for studying genes, genomes, traits, species, interactions, and even ecosystems in the view of rapid evolution. How plants adapt to environmental parameters, and how trade-offs, constraints, or pleiotropy impact this process is of interest for both basic and more applied research. Importantly, current environmental change is pertinent due to warming climate, intensified agriculture, deforesting, increased fragmentation, declining pollinators, etc. It is safe to assume that all these parameters will impact natural selection and thus adaptive evolution in nature. Therefore, it is timely to address adaptive evolution experimentally, and develop appropriate models for predicting its outcome. Such experiments can be set up in a greenhouse, allowing for great control of environmental factors, and thus great power of recognizing causative factors in evolution. Alternatively, plots can be set up in experimental fields, providing a superior natural setting, yet less easy identification of specific factors causing evolutionary change. A key question for any experimental approach is whether evolution in an artificial or manipulated ecosystem, either in the greenhouse or in the field, effectively mimics evolution in natural ecosystems.

A particularly timely example for the need to address evolutionary questions is the science of plant conservation (Olivieri et al., 2016). Models of adaptability are deeply desired in conservation biology, to predict which populations of rare plants will be able to adapt, and which need measures like assisted migration for survival (Jump and Penuelas, 2005). Rapid adaptation is also of concern in invasive species, that may threaten rare natives (Alexander, 2013). Experimental evolution can act as a kind of test for adaptability or evolutionary rescue (Gonzalez et al., 2013), as done in alpine species of Drosophila, showing a lack of ability to adapt to warmer temperatures (Kinzner et al., 2019). This approach is even more powerful when combined with genomics, in an “evolve and re-sequence” approach. In evolve and re-sequence experiments, the adaptive potential of experimental populations is tested in response to specific factors such as temperature change or drought. Subsequently, plant populations before and after evolution are genotyped and changes in frequencies of specific alleles can be assessed. Such tests of adaptability and assessment of adaptive genetic variation can yield powerful models of variation in specific genes that enable adaptation. This approach has been used in Drosophila to establish that adaptability to harsh environments is correlated to genome-wide variability, rather than patterns of inbreeding (Orsted et al., 2019). Similarly, Stelkens et al. (2014) showed in yeast that hybridization enables evolutionary rescue and adaptation to degraded environments.

Real-time evolution in botany may gain more momentum in the future by the development of new fast-cycling model plant species, analogous to the rapid cycling Brassica [Brassicaceae] species bred by Paul Williams a few decades ago. This would also help to address a greater variety of research questions in a real-time evolution context, because a few “model” species are not enough to represent the diversity of biological functions found in plants. Developing new fast-cycling models would, for example, require artificially selecting for short generation time in an annual plant, yet maintaining genome-wide genetic variability, to allow for sufficient adaptability in subsequent experiments. Besides having an annual life cycle, such plants should be easy to grow, have seeds that can be stored for long time periods, and with easy subsequent germination. Annual species of Mimulus [Phrymaceae], Consolida [Ranunculaceae], Aquilegia [Ranunculaceae], Plantago [Plantaginaceae], Helianthus [Asteraceae], and several members of the Brassicaceae and the Poaceae may be good candidates for such new models, to name just a few. Plants adapted to habitats with naturally short vegetation period, such as desert or alpine annuals, may be promising, too. Selecting for shorter generation time in any plant species may be an interesting experiment in itself, allowing quantitative genetic studies of generation time and its pleiotropic effects. New fast-cycling models would reveal fascinating opportunities for new studies that include the evolutionary dimension, something highly desirable for future botanical research.

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来源期刊
American Journal of Botany
American Journal of Botany 生物-植物科学
CiteScore
4.90
自引率
6.70%
发文量
171
审稿时长
3 months
期刊介绍: The American Journal of Botany (AJB), the flagship journal of the Botanical Society of America (BSA), publishes peer-reviewed, innovative, significant research of interest to a wide audience of plant scientists in all areas of plant biology (structure, function, development, diversity, genetics, evolution, systematics), all levels of organization (molecular to ecosystem), and all plant groups and allied organisms (cyanobacteria, algae, fungi, and lichens). AJB requires authors to frame their research questions and discuss their results in terms of major questions of plant biology. In general, papers that are too narrowly focused, purely descriptive, natural history, broad surveys, or that contain only preliminary data will not be considered.
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