Lessons on Evolution from the Study of Edaphic Specialization.
Over a century and a half after Darwin's On the Origin of Species, there is little doubt that ecological adaptation plays a crucial role in the diversification of species (Nosil, 2012). The study of ecological speciation marks a central theme in evolutionary biology, with a major focus on understanding the role of adaptation in reproductive isolation (Baack et al., 2015) and species divergence (Schemske, 2010).
Plants found on 'extreme' soils, those characterized by unusual chemical (pH, ionic strength, nutrients, or heavy metals) or physical conditions (soil moisture, temperature, texture, structure, or depth), provide model systems to examine the role of edaphic (soil-related) adaptation in ecological speciation (Rajakaruna, 2004; Kay et al, 2011) and adaptive radiation (Ellis & Weis, 2005; Paun et al., 2016; Shimizu-Inatsugi et al., 2016). The landmark papers "Evolution in closely adjacent plant populations" (Antonovics, 2006 and references therein) focused on the evolution of metal tolerance in the grasses Anthoxanthum odoratum and Agrostis tenuis on mine tailings in Europe. These classic papers, along with early studies of ecotypes on western North American serpentine soils (Anacker, 2014 and references therein), illustrated how strong selection can maintain distinct sub-populations in the face of gene flow, highlighting three key lessons from edaphic specialization pertinent to evolution: first, edaphic transitions often have direct or indirect effects on reproductive isolation between ecologically-divergent populations (Christie & Macnair, 1987; Wright et al, 2013), suggesting a link between adaptation and speciation; second, some populations can evolve (or lose) tolerance to edaphic conditions rapidly and with relative ease, suggesting that major gene loci (i.e., loci with large phenotypic effects) could be driving adaptive evolution (Macnair, 1983; Bratteler et al., 2006, 2006; Lowry et al., 2012); and third, populations within some species can independently evolve tolerance to edaphic conditions (i.e., tolerance evolves multiple times within a species), suggesting a tendency towards parallel evolution (Rajakaruna & Whitton, 2004; Ostevik et al., 2012; Roda et al., 2013). Edaphic specialists, especially plants growing in ultramafic (Harrison & Rajakaruna, 2011; Anacker, 2014), gypsum (Moore et al., 2014; Escudero et al., 2015; Bolukbasi et al., 2016), mine tailing (Ernst, 2006), seleniferous (Schiavon & Pilon-Smits, 2017), and saline (Saslis- Lagoudakis et al., 2014; Cheeseman, 2015) habitats, are now at the forefront of plant evolutionary research, providing model systems for exploring factors and mechanisms driving evolutionary processes from the species to community level (Cheplick, 2015).
In this review, I highlight studies of edaphic specialists from serpentine outcrops, saline soils, gypsum and other carbonate deposits, and heavy metal-rich mine tailings, and explore such questions as:
* How do edaphic endemics evolve (i.e., what are the major pathways to edaphic specialization)?
* Are edaphic endemics new or old species?
* How does adaptation contribute to reproductive isolation?
* Is the transition to edaphic endemism directional, and are edaphic endemics evolutionary dead-ends?
* Does parallel evolution of traits conferring adaptations and reproductive isolation occur frequently in edaphic specialists?
* How does tolerance to edaphic extremes influence competitiveness in 'normal' soils, i.e., what is the cost of tolerance?
* Do interactions with herbivores or microbes drive the evolution of edaphic specialization?
* Are edaphic specialists more or less sensitive to climate change?
* What is the genetic basis of edaphic specialization and speciation? Is there evidence for horizontal gene flow conferring edaphic adaptation or for genetic similarity among the mechanisms used by different species under any given edaphic stress?
Finally, I outline directions for future research on the use of edaphic specialists as model systems to study evolutionary processes across cellular, organismic, population, and community levels.
How do Edaphic Endemics Evolve?
Colonization of new environments, including edaphic islands, can be achieved by ecotypic differentiation via local adaptation or by phenotypic plasticity (Hereford, 2009; Palacio-Lopez et al., 2015). Early studies in Sweden (Turesson, 1922) and California (Clausen et al., 1940) demonstrated that local adaptation is common in species distributed across altitudinal and climatic gradients. Similarly, elegant transplant experiments conducted by the British Ecological Society from the 1920s to the 1930s highlighted edaphic factors as potent agents of selection (Marsden-Jones & Turrill, 1938). The long-term Park Grass Experiment in Rothamsted, UK (Silvertown et al., 2006), in which the grass Anthoxanthum odoratum was subjected to different fertilizer and lime treatments across multiple plots, showed local adaptation to soil types over a relatively short period. These studies exemplified how experimental methods such as common garden and reciprocal transplant experimentation can be used to examine how phenotypic plasticity and local adaptation contribute to habitat specialization (Wright & Stanton, 2011).
Species living in harsh environments, including on edaphic islands, have genotypes either broadly tolerant to wide-ranging environmental conditions (Bradshaw, 2006) or locally adapted to specific ecological factors characteristic of the 'home' environment, i.e., ecotypes (Lowry, 2012). Ecotypes are a critical stage in the speciation process, and the recognition of such populations is vital for evolutionary studies (Via, 2009). The existence of sharp habitat boundaries between ecotypes is a compelling phenomenon that has provided some of the best experimental evidence of natural selection in the wild (Rajakaruna & Whitton, 2004). Although there is much support for ecotypic differentiation and species-level endemism among flowering plants found on edaphic islands (O'Dell & Rajakaruna, 2011), such edaphic specialization is not as well- documented among ferns, gymnosperms, mycorrhizal fungi, lichens, or bryophytes (Rajakaruna et al., 2014).
It is important to examine factors and mechanisms driving rapid evolution in response to environmental pressures, such as those influencing plants on edaphic islands. Still, it is equally critical to pay attention to 'genostasis,' in which the lack of sufficient genetic variation may result in evolutionary failure (Bradshaw, 1991). Early work on mine tailings (Antonovics, 2006 and references therein) provides an example: at edges of mine tailings, some species maintain heavy metal-tolerant and - intolerant genotypes located only a few centimeters apart. In many other adjacent species, such edaphic differentiation is not found. Most species found off of mine tailings are unable to colonize metal-contaminated soil because they do not have the necessary alleles for adaptive variation (Antonovics, 1976). Additionally, a meta-analysis of studies of local adaptation showed that only 45% of population pairs (out of 1,032 compared) had better performance of the 'home' population relative to the 'away' population at both sites (Leimu & Fischer, 2008). This suggests that habitat-mediated selection may not be as common in plants as generally assumed. Lack of local adaptation may result from reasons other than the lack of necessary genetic variance (Bell, 2012; Cheplick, 2015), including insufficient time for adaptive evolution, a high degree of phenotypic plasticity, extensive gene flow, and random genetic drift due to founder events. Further, lack of local adaptation may be a statistical/methodological artifact of choosing study habitats that are too similar in their major selection pressures (Cheplick, 2015).
Landmark papers on factors and mechanisms driving habitat specialization (Mason, 1946a, b; Raven, 1964) provided an early framework for understanding the role played by soil-based selection in the origin of new species. These ideas offered a context to envision a set of stages that may lead to the establishment of an edaphically endemic species, from the initial tolerance of an edaphic condition by preadapted genotypes to clear-cut species formation (Kruckeberg, 1986). While this sequence represents a relatively precise picture of the evolutionary pathways to endemism, it does not indicate why some genotypes evolve through all the steps and others do not. It is possible that there is a relatively higher cost of broad tolerance in edaphic endemic species relative to the cost of tolerance found in widespread taxa with broad edaphic tolerance (Kazakou et al., 2008; Maestri et al., 2010). Thus, only lineages experiencing a high cost of broad tolerance will be subjected to strong divergent selection across an edaphic boundary, leading to evolution of ecotypes and edaphic endemic species. The decisive step distinguishing an ecotype from an endemic species is likely the acquisition of complete reproductive isolation between the ancestral population and the ecotype, allowing an independent gene pool to evolve (Macnair & Gardner, 1998; Lowry, 2012). Flow this occurs, especially when populations are not geographically isolated, is a fundamental question in speciation research (Kay et al., 2011; O'Dell & Rajakaruna, 2011).
Populations that become geographically isolated can gradually acquire genetic differences through selection and drift, and eventually become reproductively isolated through the process of allopatric speciation. Past climate fluctuations and other dramatic environmental changes may have led to the extinction of widespread populations due to massive vegetation shifts such as those that occurred during postglacial reforestation (Slovak et al, 2012). Those surviving relict populations, especially those isolated on edaphic islands, may have become differentiated by means of allopatric speciation. Further, chance dispersal into novel edaphic habitats, particularly during strong climatic oscillations of the Quaternary, would have also provided conditions of relaxed competition, facilitating the evolution of edaphic specialization (Dillenberger & Kadereit, 2013). Thus, allopatric speciation may be a particularly important pathway for the origin of edaphically restricted paleoendemic species (Table 1). Abrupt and sharply delineated edaphic habitats often provide opportunities for the divergence of edaphic specialist species along contact zones through the process of parapatric speciation (Table 1). There are major challenges, however, in demonstrating a parapatric origin for a species, as speciation must occur without a geographic barrier to gene flow. First, it is possible that the initial evolution of traits driving reproductive isolation may have occurred under allopatric conditions (Pettengill & Moeller, 2012); a new species that evolved under allopatry may subsequently come into contact along an edaphic boundary and appear identical to parapatric species in being relatively young, ecologically divergent, and reproductively isolated. Further, reinforcement of reproductive isolation (Pfennig & Pfennig, 2009), a process by which selection can minimize maladaptive hybridization, may take place upon contact with those populations that initially diverged under allopatry, thereby completing the speciation process. Genetic analyses can help distinguish whether divergence first occurred in allopatry and speciation was completed by reinforcement (Widmer et al, 2009), although extensive introgression and hybridization following secondary contact may make such determinations difficult (Barraclough & Vogler, 2000; Ortiz-Barrientos et al., 2009; Strasburg et al., 2012). How speciation can proceed in the face of gene flow between potentially interbreeding populations, including among parents and newly formed hybrid species (Andrew et al., 2012; Renaut et al., 2013), is especially revealing of the challenges associated with habitat specialization under parapatry. Gene flow can dilute the adaptive differences that selection generates between divergent populations; this may be especially problematic when one population is significantly larger than the other, as in the case of a newly divergent population found adjacent to an ancestral population, or in the presence of asymmetric gene flow (Ellstrand, 2014). However, if the edaphic condition confers strong selection pressures on one side of the edaphic barrier and there is strong selection against the tolerance genes on the other side of the edaphic boundary (i.e., low 'Haldanian' fitness), then one could expect evolution to occur even in the presence of gene flow.
Similarly, case studies of sympatric speciation (i.e., evolution from a single ancestral species in the same location) must demonstrate species co-existence, sister relationships, reproductive isolation, and that a former allopatric phase is highly unlikely. In two palm species of Howea, endemic to the remote Lord Howe Island, Australia, divergence in blooming periods is strongly correlated with soil type; only a few genetic loci are more divergent between the two species than expected under neutrality, a finding consistent with sympatric speciation involving disruptive or divergent selection (Savolainen et al., 2006; Fig. la). Morphotypes of the palm Geonoma macrostachys in Peruvian lowland forests provide another example of sympatric speciation likely occurring between ecologically divergent (via soil and light) and reproductively isolated (via phenology and pollinators) populations (Borchsenius et al., 2016).
Budding or peripatric speciation is a diversification process through which new species form at the periphery of an ancestral population. In this case, a few preadapted genotypes encounter and colonize an edaphic island resulting in edaphic specialization. Budding speciation appears to be especially common in plants (Crawford, 2010), as high rates of selfing (Antonovics, 1968) and polyploidization (Soltis et al., 2004) result in abrupt reproductive isolation between the ancestral and derivative populations. As the initial peripheral populations are small, they can often quickly acquire reproductive isolation via catastrophic selection, i.e., differential survival during an episode of mass extinction (Gottlieb, 2004), or strong divergent selection (Grossenbacher et al., 2014). At the time of speciation, sister taxa will exhibit highly asymmetrical and completely or partially overlapping distributions, yet occupy distinct microhabitats (Gottlieb, 2004), such as edaphically contrasting microsites. Eighty percent of the sister species of Mimulus show patterns consistent with budding speciation: pairs are broadly sympatric, have highly asymmetric distributions, and occupy distinct habitats (Grossenbacher et al., 2014), suggesting that ecologically divergent taxa in this genus (Lowry et al., 2008) may have arisen from budding or peripatric speciation (see Table 1 for additional case studies).
A meta-analysis of phylogenies available for plants in the California Floristic Province (CFP) showed that of 71 sister pairs from 12 families, 57 pairs (80%) were broadly sympatric (Anacker & Strauss, 2014). Range sizes of sisters differed by a mean of 10-fold and range overlap and range asymmetry were greatest in younger sisters, suggesting that in the CFP, budding speciation has been an important pathway for the origin of neoendemic species. Interestingly, of the 71 sister pairs they examined, 29 (41 %) showed complete edaphic shifts whereas 20 (28%) showed partial edaphic shifts, strongly implying that budding speciation via edaphic specialization is commonplace in the edaphically-heterogeneous landscape of the CFP. Similarly, in the Cape Floristic Region (CFR) of South Africa, 87% of sister species show partial or complete ecological shifts; however, complete edaphic shifts were found in only 17% of CFR pairs (van der Niet & Johnson, 2009) versus in 41% of the CFP pairs. This difference may be attributable to lower levels of edaphic and topographic heterogeneity in the CFR compared to the CFP, likely making edaphic transitions less significant in speciation (Anacker & Strauss, 2014).
Hybridization, with or without polyploidy, can play a critical role in the origin and establishment of edaphic specialists (Abbott et al., 2013; De Storme & Mason, 2014), especially under parapatric, sympatric, and peripatric modes of speciation. Studies of the relative importance of hybridization and polyploidization on the origin of edaphic endemics show that introgression between close relatives and subsequent adaptation of hybrid offspring to novel edaphic conditions, when directly or indirectly resulting in reproductive isolation with parental taxa, can result in the origin and establishment of hybrid species (Table 1). Edaphic divergence of the hybrid species from its parental taxa appears to be central to the successfitl origin of several hybrid species, occurring even in the absence of post-zygotic isolation caused by chromosomal and other genetic incompatibilities (Abbott et al., 2010). There is strong evidence, via reciprocal transplant and common garden approaches, for greater fitness of a hybrid in a novel edaphic habitat relative to that of parental taxa for the sand dune specialist Helianthus anomalus and the salt marsh specialist H. paradoxus (Fig. 1 b), although such conclusive evidence is lacking for another hybrid species, H. deserticola (Edelist et al., 2009; Donovan et al., 2010). Similarly, a Salix hybrid complex from the European Alps has greater tolerance to cold temperatures and nutrient-poor/low pH soils than either parent (Gramlich et al., 2016). The hybrids appear to have originated after glaciers retreated and established persistent populations within a few decades. A major factor contributing to hybrid establishment under sympatric settings is the ability to occupy more extreme edaphic niches relative to either parent species (Abbott et al., 2010; Gramlich et al., 2016).
Are Edaphic Endemics New or Old Species?
Edaphic specialists, formed through the multiple modes described above, have often been used to compare the relative importance of rapid versus gradual speciation in the origin of endemic species (Pepper & Norwood, 2001; Anacker, 2014). Edaphic specialists can arise under both of these scenarios (i.e., rapid versus gradual). Recently evolved neoendemics can evolve from nearby, non-specialized relatives via rapid and local speciation, including via parapatric, sympatric, and peripatric modes (Anacker & Strauss, 2014; Ferris et al., 2014; Schneider et al., 2016). In contrast, ancient paleoendemics may have evolved via gradual speciation through biotype depletion, including via allopatric (vicariant) speciation, as has been shown for the Streptanthus glandulosus complex (Mayer & Soltis, 1994), Caulanthus amplexicaulis var. barbarae (Pepper & Norwood, 2001), and for Minuartia spp. (Moore et al., 2013; Moore & Kadereit, 2013; Table 1). There is ample evidence from studies of edaphic specialists that large-scale geographic isolation is not always critical for diversification; total reproductive isolation can be achieved even in the face of gene flow (Antonovics, 2006). In fact, recent phylogenetic investigations suggest that neoendemism may be the norm in cases of edaphic specialization, not the exception (Baldwin, 2014). Peripatric or budding speciation is an especially common mode of speciation among neoendemic edaphic specialists, with high rates of selfing and polyploidization causing immediate reproductive isolation between adjacent yet edaphically distinct populations (Gottlieb, 2004). Strong directional and disruptive selection that often occurs across edaphic boundaries, combined with parallel changes contributing to reproductive isolation between divergent populations, can lead to rapid and local speciation (Levin, 1993; Crawford, 2010). In peripatric speciation, the progenitor species is initially paraphyletic; however, lineage sorting and extinction will eventually result in monophyly (Crawford, 2010). Case studies of edaphic differentiation in which there are phylogenetic or population genetic data to support relatedness between edaphically divergent taxa are listed in Table 2 along with additional evidence for edaphic divergence via ecological, physiological, reproductive, or genetic studies (when available).
How Does Adaptation Contribute to Reproductive Isolation?
Establishing a direct or indirect link between traits that confer edaphic adaptation and traits that contribute to reproductive isolation is strong evidence for the role of edaphic factors in the divergence of species (Hopkins, 2013; Wright et al., 2013). Classic studies of plants on mine tailings in Europe (Antonovics, 2006 and references therein) clearly demonstrated that rapid and repeated evolution of metal tolerance is often associated with the evolution of prezygotic isolating mechanisms, including the evolution of both self-compatibility (Mousset et al, 2016 and references therein) and earlier flowering in metal-tolerant populations (Antonovics, 2006 and references therein). Both of these traits significantly limit gene flow between divergent populations, aiding in the evolution of independent gene pools under strong edaphic selection. Flowering time shifts in Anthoxanthum odoratum in the Park Grass Experiment, at the boundaries between plots vastly varying in soil pH, have resulted in reduced gene flow (Silvertown et al., 2005). Adjacent populations that had a common origin at the start of the experiment in 1856 have now diverged at neutral marker loci, suggesting that reinforcement (i.e., selection against maladaptive hybridization) has been key to completing speciation. Establishing a direct link between pH tolerance and flowering time is necessary to confirm the role of such reinforcement in speciation. Interestingly, there was no indication of reinforcement at the boundaries of plots with smaller pH differentials, suggesting a link between pH preference and flowering time. Earlier flowering times have often been documented for serpentine-associated taxa, including those in the Lasthenia californica complex (Yost et al., 2012), Helianthus exilis (Sambatti & Rice, 2007), Mimulus spp. (Macnair & Gardner, 1998; Selby et al, 2014), Gilia capitata (Kruckeberg, 1951), and Lep to siphon spp. (Kay et al., 2011). Near complete reproductive isolation between coastal and inland populations of Mimulus guttatus has been achieved by selection against immigrants and flowering time differences (Lowry et al, 2008). The annual, inland populations exposed to more summer drought flower early compared to the perennial populations along the coast on more moist soils. Diversification within the stone plant genus Argyroderma of the Western Cape Province in South Africa also appears to have occurred through allopatric adaptive speciation, under strong edaphic-mediated divergent selection along with reproductive isolation achieved through divergence in flowering times (Ellis et al., 2006). In the well documented case of sympatric speciation in Howea, the shift in flowering phenology between species on volcanic and calcareous soils dramatically reduced interspecific gene flow (Hipperson et al., 2016; Fig. la). There also appears to be a pleiotropy between flowering time and adaptation to drought, salinity, and pH, driving speciation (Dunning et al., 2016). Temporal isolation is a key factor in facilitating plant speciation; however, flowering time differences between close relatives can arise as a flexible response to divergent edaphic conditions (Levin, 2009) or through direct or pleiotropic genetic effects of edaphic adaptations (Hunter & Bomblies, 2010; Selby et al., 2014).
Soil constituents, such as heavy metals, are directly implicated in causing reproductive isolation between close relatives. Copper tolerance in Mimulus guttatus is expressed in the sporophyte as well as in the pistil (Searcy & MacNair, 1993). Copper in the pistils acts as a selective agent since seed production is reduced when pollen donors are maladapted to copper-rich soils (Searcy & Mulcahy, 1985; Searcy & MacNair, 1990). Metal accumulation in reproductive organs generates a strong prezygotic isolating mechanism by decreasing reproductive output in crosses between edaphically divergent parents. Therefore, edaphic factors directly act as reproductive barriers, favoring reproduction between plants growing under similar edaphic conditions and minimizing gene flow between edaphically divergent taxa.
Serpentine tolerant Brassicaceae endemics can limit nickel uptake into the shoot, particularly into reproductive organs, while non-endemics accumulate significantly more nickel into reproductive organs relative to shoots (Meindl et al., 2014). In the selenium hyperaccumulating Stanleya pinnata, selenium is preferentially allocated to flowers, while the non-accumulating relative Brassica juncea has higher selenium concentrations in leaves relative to flowers (Quinn et al., 2011a). Selenium had no effect on pollen germination in the hyperaccumulator, but it impaired pollen germination in the relative, showing a possible evolutionary cost for selenium accumulation through decreased pollen germination in the non-accumulating taxon.
Pollinators can distinguish between 'clean' nectar and that contaminated with metals, and avoid nectar enriched with metal because of toxicity (Meindl & Ashman, 2013). Pollinator preference of nectar, therefore, can potentially limit gene flow between close relatives found on distinct substrates. Additional trait differences between edaphically divergent taxa can also act as reproductive barriers, including flower size differences leading to differential pollinator preferences (Gardner & Macnair, 2000) and pollen-stigma incompatibilities leading to reduced potential for fertilization (Rajakaruna & Whitton, 2004).
Edaphic specialists also provide opportunities for examining how post-zygotic isolating mechanisms contribute to edaphic divergence. In the Mimulus guttatus complex, there is evidence for inviability in hybrids between metal-tolerant and intolerant parents (Gardner & MacNair, 2000), although such post-zygotic isolation is not a factor between coastal and inland ecotypes of the same taxon (Lowry et al., 2008). Work on copper tolerance in M. guttatus (Macnair & Christie, 1983; Wright et al., 2013) has revealed a genetic association between edaphic tolerance and hybrid inviability (Fig. 1c). In Collinsia sparsiflora, ecotypic adaptation to serpentine is associated with the expression of hybrid sterility between serpentine and nonseipentine ecotypes, over spatial scales of less than 1 km (Wright & Stanton, 2007; Moyle et al., 2012; Fig. Id). Further, allozyme (Wright & Stanton, 2011) and microsatellite data (Moyle et al., 2012) suggest there is little genetic differentiation between ecotypes, indicating that hybrid sterility may have recently evolved.
A potentially fascinating example of the relationship between adaptation and reproductive isolation yet to be studied lies in the progenitor-derivative species pair of Layia glandulosa subsp. lutea and L. discoidea (Baldwin, 2005). Unlike Mimulus, in which hybrid lethality has been documented between copper-tolerant and -intolerant taxa (Wright et al., 2013), there is complete fertility between artificial crosses of the serpentine-intolerant and serpentine-endemic Layia species; however, spontaneous hybrids are not found in nature, suggesting that partially or completely reduced hybrid fitness in one or both parental habitats may be responsible for the diversification. Additionally, it is unknown whether the flower shape (discoid- vs. ray-flowered) plays a role in pollinator preferences or whether potential differences in flowering time, especially when populations occur along contact zones, contribute to pre-zygotic isolation. Similarly, factors contributing to reproductive isolation between the guanoendemic Lasthenia maritima and its close relative, the coastal bluff-specialist L. minor, are little-known (Rajakaruna, 2004). There is evidence for greater self- compatibility within the guano-endemic (Crawford et al., 1985), resembling the trends shown for some metal-tolerant species (Mousset et al, 2016 and references therein); however, it is unclear whether other isolation barriers, such as differences in pollinators or flowering times, or hybrid lethality and reduced fitness of hybrids in parental habitats, also contribute to preserving isolation. Further, the physiological bases for guano adaptation are also unknown. Whether the high nutrient content (nitrogen, phosphoms), low pFI (due to uric and other acids), or some other chemical or physical factor of guano drives selection on these substrates needs further investigation. For both Layia and Lasthenia case studies, QTL-based comparative genome mapping and transcript profiling approaches (Sun & Schliekelman, 2011) can be used to determine whether any traits conferring adaptation to substrate have effects on traits contributing to reproductive isolation between the divergent taxa.
Are Edaphic Endemics Evolutionary Dead-Ends?
The growing availability of molecular phylogenies has provided us with means to investigate the evolutionary dynamics of habitat specialization (Vamosi et al., 2014), including directionality of evolution of edaphic endemism (Anacker et al, 2011). Population genetic and phylogenetic analyses of serpentine-tolerant plants (Mengoni et al., 2003a, b; Nyberg Berglund et al., 2004; Anacker, 2011), metallophytes (Mengoni et al, 2001; Pauwels et al., 2005), halophytes (Bennett et al., 2013), calciphiles (Klein & Kadereit, 2015), and gypsophiles (Bresowar & McGlaughlin, 2015) have demonstrated that tolerance to edaphic conditions has been gained numerous times within various groups of angiosperms and has even been lost in some groups, suggesting that traits conferring edaphic tolerance are evolutionarily labile. Further, differences in the evolutionary dynamics (i.e., gains vs. losses) of edaphic tolerance documented among different lineages may result from association of edaphic tolerance traits with other ecophysiological traits related to tolerance of environmental stresses, with edaphic tolerance being more easily gained in preadapted lineages (Saslis-Lagoudakis et al, 2014; Selby et al, 2014). The direction of serpentine endemism among genera with serpentine-tolerant species in California is mostly from non-tolerant and - tolerant species to endemic species, with a few reversals from the tolerant or endemic state to the non-tolerant state (Anacker et al, 2011). This suggests that the evolution of edaphic endemism may represent an evolutionary dead-end. This may not always be the case, however, as endemics are often able to influence adjacent populations by repeated episodes of introgression and polyploidization. In the diploid-tetraploid complex of Knautia arvensis, recurrent polyploidization within serpentine populations followed by hybridization with the neighboring non-serpentine tetraploid populations, has allowed serpentine tetraploids to escape from their serpentine refuge and spread further into non-serpentine habitats (Kolar et al., 2012). Similarly, endemic Streptanthus clades are often quite diverse, with endemism having evolved numerous times and having been lost at least once (Cacho et al., 2014). In Arabidopsis, there is also evidence for serpentine-tolerant loci being introgressed from one serpentine-endemic to another (Arnold et al, 2016) and for hybridization between two sympatric and diploid limestone endemics, giving rise to a tetraploid siliceous soil endemic (Schmickl & Koch, 2011). These findings suggest that edaphic endemism does not always represent an evolutionary dead-end and that endemics have the potential to further diversify within (Cacho et al., 2014) or across substrates (Schmickl & Koch, 2011).
How Does Tolerance to Edaphic Extremes Influence Competitiveness in 'Normal' Soils?
Edaphic islands have long been considered a refuge from competition (Kruckeberg, 1954), suggesting that tolerance to edaphic extremes has a cost. However, the idea of a trade-off of competitive ability for tolerance (i.e., trade-off hypothesis) needs close scrutiny via experimentation (Harper et al., 1997a). Edaphic specialists, compared to non-specialists, often appear to be less competitive (Milla et al., 2011; Moore et al., 2013; Anacker, 2014; Bastida et al, 2014) and more susceptible to herbivory when found on 'normal' soils (Dechamps et al, 2008; Kay et al., 2011; Strauss & Boyd, 2011). However, plants that specialize in a particular edaphic setting (e.g., a metal mine) may have adapted not only to the increased metal concentrations but also to other stressors such as drought, low nutrients, high light, and poor soil structure characterizing the mine site. Therefore, it is unclear if a reduction in fitness or competitive ability results from the direct cost associated with metal tolerance per se (i.e., trade-off hypothesis) or with other correlated traits conferring adaptation to the mine site. To demonstrate that a negative correlation between traits is the result of pleiotropy (and not via gene/s in linkage disequilibrium with metal tolerance gene/s) it is essential to experimentally demonstrate that the traits are genetically correlated (Partridge & Sibly, 1991). Experimental studies on copper tolerance in Mimulus guttatus (Harper et al., 1997a), however, provide no clear evidence in support of a trade-off hypothesis. Additionally, low fitness of metal tolerant plants in 'normal' environments can also result from an increased metabolic requirement for the metal (i.e., metal requirement hypothesis). Studies conducted on M. guttatus, however, show no such increased requirement for copper (Harper et al., 1997b, 1998), suggesting that neither the tradeoff hypothesis nor the metal requirement hypothesis can ftilly explain the cost of copper tolerance in M. guttatus. Additional experimentation will likely reveal that it is not one trait but a suite of adaptive traits (i.e., genes, their modifiers, and the interactions between them; see Smith & Macnair, 1998) that has a cost in a 'normal' habitat. Similarly, there is little evidence of a cost for tolerance to either low soil calcium to magnesium ratios or high concentrations of heavy metals, two key selective pressures experienced by plants growing on serpentine soils (Brady et al., 2005; Kay et al., 2011). Serpentine endemics, however, are typically slow-growing and stress-tolerant, rather than fast-growing and what is typically considered as competitively superior (Anacker & Harrison, 2012; Fernandez-Going et al., 2012), consistent with the notion of a tradeoff between competitive ability and tolerance to serpentine. Indigenous resistant plants on serpentine soil have less competition from invasive species when growing on serpentine soil (Harrison, 1999; Gram et al., 2004; Going et al., 2009), but are poor competitors on high-nutrient soils (Rice, 1989; Jurjavcic et al, 2002; Vallano et al., 2012). Regardless, the evidence that competition is reduced on serpentine soils (Moore & Elmendorf, 2011) and that edaphic endemics are competitively inferior is not substantial (Powell & Knight, 2009; Fernandez-Going & Harrison, 2013). Furthermore, these hypotheses of a cost of tolerance have not been tested in numerous lineages, nor have they been examined across distinct substrate types.
Comparing pairs of sister taxa could help reveal the evolutionary costs of habitat specialization relative to broad tolerance and address why some species become edaphic specialists whereas others maintain general-purpose genotypes (sensu Baker, 1965) that can tolerate wide-ranging habitat conditions. A widely-distributed Aquilegia subspecies has greater adaptive phenotypic plasticity and higher competitive ability than a related taxon that is a narrow endemic (Bastida et al., 2014). This suggests that adaptive plasticity, competitive ability, and lineage history all contribute to phenotypic divergence, edaphic niche specialization, and range distribution.
The hypothesis of a greater cost of tolerance and resulting trade-offs in competitive ability is, however, gaining recognition as a potentially important driving force in the evolution of edaphic endemism. The integration of molecular phylogenies with descriptive and experimental ecological data reveals that occupation of bare habitats is a precursor for serpentine specialization in Streptanthus and close allies (Cacho & Strauss, 2014) and may be central to soil specialization. When comparing ancestor-derivative species pairs, it was evident that shifts onto serpentine soils were not from soils with a low calcium to magnesium ratio or high nickel content (like those characteristic of serpentine soils) but from bare microhabitats. Preadaptations to features characterizing bare habitats, including water stress, combined with inherently lower competitive ability, perhaps due to increased investment for defense (Strauss & Cacho, 2013), may have enabled the colonization of serpentine (also, see von Wettberg et al., 2014), leading to multiple origins of serpentine adaptation among Streptanthus and allies (Armbmster, 2014). Whether such preadaptation to bare habitats is a precursor for adaptation to other rock outcrop plant communities can be tested via similar approaches, using a combination of molecular phylogenetic and ecological data (Cacho & Strauss, 2014).
Does Parallel Evolution Occur Frequently in Edaphic Specialists?
Parallel (or repeated) evolution provides strong evidence for the role of ecology in driving divergence (Nosil, 2012). Parallel edaphic adaptation may be achieved via the evolution of novel alleles contributing to specialization or via parallel increases in the frequency of alleles (Faria et al., 2014). Repeated evolution of traits may not be unusual in clades that have undergone ecological radiation, particularly in those taxa adapted to environments imposing strong divergent selection such as harsh edaphic environments (Levin, 2001; Mengoni et al., 2003a, b). When changes in edaphic tolerance are associated with changes in reproductive compatibility, a case for parallel ecological speciation can be made (Rajakamna & Whitton, 2004). Contrary to these findings, there are only a limited number of studies showing the repeated evolution of traits conferring adaptation and reproductive isolation in plants, i.e., parallel ecological speciation (Ostevik et al., 2012). Interestingly, of the 23 potential cases for parallel ecological speciation cited by Ostevik et al. (2012), 10 are from plants adapted to harsh edaphic conditions (see Table 1 in Ostevik et al, 2012). The prevalence of cases of edaphic adaptation among the limited number of studies of parallel ecological speciation suggests that parallel evolution appears to occur more often in, or is better known from, edaphic specialists relative to other species. Genomic methods can play an important role in determining whether parallel (via independent evolution of the same or different genes; Nichols & McNeilly, 1982; Levin, 2001; Rajakamna et al, 2003c) or horizontal gene flow of clustered genes (via introgression; Arnold et al, 2016) are responsible for the parallel evolution of edaphic tolerance.
Do Interactions with Herbivores or Microbes Drive the Evolution of Edaphic Specialization?
Plant interactions with other organisms, including those that are mutualistic and antagonistic, appear to have a role in edaphic specialization (Strauss & Boyd, 2011; Van Nuland, 2016). Harsh soils, which are often nutrient-poor, water-stressed, trace-element rich, and found in barren and open landscapes, may increase physiological costs associated with herbivore damage as well as make plants more conspicuous to herbivores (Strauss & Boyd, 2011). Edaphic specialists may be more susceptible to herbivory than their non-specialist relatives and plant-herbivore interactions can sometimes be central to edaphic specialization (Fine et al., 2004; Van Zandt, 2007; Lau et al., 2008). Increased herbivore pressure due to increased noticeability on rock outcrops can drive increased investment in defense strategies among edaphic specialists (Strauss & Cacho, 2013). The high costs of defense can result in trade-offs in plant competitiveness (Fine et al., 2006) and restrict plant distributions on harsh soils, contributing to high rates of edaphic endemism. Similarly, the pathogen refuge hypothesis (Kruckeberg, 1992; Springer, 2007) suggests that plants will experience lower disease pressure on serpentine and other edaphically harsh environments, either through reduced disease transmission rates in sparsely populated serpentine plant communities (Thrall et al., 2007) or through lowered disease-associated damage, as has been shown for serpentine-adapted Hesperolinon (Springer, 2009). Serpentine specialists within Hesperolinon are less susceptible to fungal infection, perhaps due to their ability to selectively uptake calcium, which is required to initiate an effective immune response. Less specialized species appear to be more susceptible to fungal disease on serpentine soil (Springer, 2007, 2009). Such a pathogen-refuge effect might also reinforce edaphic associations among plants and promote greater edaphic specialization. In parapatric coastal populations of Senecio lautus, herbivores have a central role in preventing gene flow in the field via differential seedling predation of both migrants and hybrids, whereas soil elemental content contributes to divergent selection on populations both locally and on a geographic scale (Melo et al., 2014).
Specialization in plant host-symbiont-soil interactions may also facilitate plant adaptation to edaphic stress and subsequent specialization (see Table 2 in Van Nuland, 2016). Arbuscular mycorrhizal fungi (AMF) are common root symbionts that can increase a plant hosts' establishment and growth in edaphically-stressful environments (Palacio et al., 2012; Schechter & Branco, 2014; Southworth et al., 2014). There are plant and microbial symbionts that enhance plant adaptation to edaphic stress (Thrall et al., 2007), showing that co-adapted interactions may play a role in edaphic specialization. For example, arsenic-tolerant AMF suppress high-affinity arsenate/ phosphate transport in the roots and decreases arsenic uptake by the arsenic- tolerant grass, Holcus lanatus, showing that arsenic-tolerant AMF may contribute to enhanced arsenic-tolerance in the metal-tolerant populations of the grass (Gonzalez- Chavez et al., 2002). However, salt-tolerant Acacia species from a high-salinity environment are less dependent on Rhizobium bacteria than salt-sensitive hosts from less stressful environments, suggesting plant-rhizobial mutualisms may be less important in plant adaptation to salinity (Thrall et al., 2008). Arbuscular mycorrhizal fungal assemblages associated with serpentine and non-serpentine ecotypes of Collinsia sparsijlora showed that plant ecotypes are associated with distinct AMF assemblages (Schechter & Bmns, 2008); however, a common garden test of host-symbiont specificity provided no evidence of adapted host ecotype-AMF specificity, suggesting that soil type, not microbial specificity, is key to determining AMF assemblage structure in C. sparsijlora (Schechter & Bmns, 2013). Findings on plant host-microbial symbiont specificity and the role of AMF on edaphic stress tolerance in higher plants are variable (Thrall et al., 2008; Glassmand & Casper, 2012); some AMF, however, have the capacity to confer metal tolerance in some plant host species either via sequestration or by contributing to growth enhancement via increased nutrient acquisition (Schechter & Branco, 2014). Such mutualistic interactions are clearly beneficial for some plant species, allowing them to colonize harsh soils and thus setting the stage for potential divergence.
The ecological and evolutionary significance of metal hyperaccumulation has received much attention (Boyd, 2014). The selective pressure for resistance to pathogens and herbivores may also result in fixation of metal hyperaccumulating trait(s) in plant populations (Boyd, 2007; Horger et al., 2013). Metal (and metalloid) hyperaccumulation has a profound effect on cross-kingdom interactions (El Mehdawi & Pilon-Smits, 2012; Boyd, 2014) as metal-hyperaccumulating plants offer a specialized niche for metal-tolerant herbivores, pollinators, microbes, and neighboring plants. For example, high levels of metal in plant tissues reduce herbivory (Quinn et al., 2010) and pathogen infection (Fones et al, 2010) and result in increased litter decomposition by specialized microbes (Quinn et al, 2011b), causing an elemental allelopathic effect on metal-intolerant neighbors (El Mehdawi et al, 2011); all these effects can influence the fitness of plants accumulating the metal, thereby contributing to edaphic specialization. Plant-microbe interactions may also influence gene flow between divergent populations due to microbe-assisted edaphic differentiation. A study of an Artemisia hybrid zone in central Utah showed that the microbial community influenced the performance of parental and hybrid plants in native and nonnative soils, segregating the distinct populations and likely contributing to their edaphic divergence (Miglia, 2007).
Metal-hyperaccumulator plants found on serpentine and other metal-rich environments are hosts to insects that appear to have co-evolved with them (Boyd, 2014). Some of these insects do accumulate heavy metals to toxic levels (Boyd, 2007) and may use them as defense against natural enemies (i.e. elemental defense hypothesis; Boyd, 2007). Although only one study supports this hypothesis (Boyd & Wall, 2001), little research regarding this hypothesis has been conducted to date. There is also no overwhelming evidence for a cost of hyperaccumulation in terms of reproductive functions or pollinator visitation. For example, pollinators of Stanleya pinnata, a Sehyperaccumulator, showed no visitation preference between high- and low-Se plants, suggesting greater tolerance to the metalloid (Quinn et al., 2011a). Whether the presence of aluminum and nickel in nectar of Impatiens capensis alters foraging behavior by bumblebees has also been investigated (Meindl & Ashman, 2013). The presence of aluminum in nectar did not influence foraging patterns; however, flowers containing nickel-laden nectar solutions had shorter visits relative to controls, and even resulted in reduced visitation of nearby nickel-contaminated flowers. Reduced visitation by native pollinators has also been documented for Streptanthus polygaloides (Meindl & Ashman, 2014) which accumulates nickel in pollinator rewards such as nectar and anthers. Although heavy metal effects on plant-pollinator interactions are clearly context-dependent, edaphic features, such as heavy metal concentrations, have the capacity to influence gene flow and reproductive isolation between close relatives through pollinator selection.
Are Edaphic Specialists More or Less Sensitive to Climate Change?
Species can respond to climate-associated stressors via both phenotypic plasticity and local adaptation (Valladares et al., 2014). Edaphic specialists, many of which display largely disjunct but widespread distributions, are ideal models for exploring how climate interacts with edaphic factors to influence plant distribution (Damschen et al., 2010; Sanchez et al., 2017). It is easy to envision how an altered climate regime can have differential effects on populations of an ecologically widespread taxon. For example, serpentine populations are generally better-adapted to low moisture conditions typical of their mostly exposed, rocky, and shallow soils (Wu et al., 2010) and may be able to withstand increased aridity and high temperatures. Therefore, under a drying climate, as is predicted for some parts of the world, nonserpentine populations may be extirpated, whereas serpentine populations, already preadapted to aridity, could survive and become endemic due to the extinction of the more widespread nonserpentine populations (Moore et al., 2013; but see Anacker, 2014). Pronounced climatic oscillations of the Quaternary period appear to have forced populations of Sempervivum, Jovibarba, and Adenostyles to respond via latitudinal or altitudinal shifts into edaphically unsuitable but relatively competition-free habitats (Klein & Kadereit, 2015). This set the stage for the divergence of edaphically specialized species via allopatric speciation. A similar scenario is presented for the evolution of the edaphically specialized Lilium pyrophilum (Douglas et al., 2011).
There is increasing evidence that climatic and edaphic factors interact to control local adaptation and substrate endemism (Fernandez-Going, 2014). Serpentine endemism peaks in wet regions both in California and some other parts of the world (Anacker, 2011; Femandez-Going, 2014), likely due to increased competition on 'normal' substrates under more productive climates. At the community level, there is also more species, functional, and phylogenetic turnover across edaphic boundaries in mesic relative to arid regions of California (Anacker & Harrison, 2012). Furthermore, serpentine endemics in California generally occupy wetter regions than even their closest relatives (Femandez-Going, 2014), but this is only true in the case of neoendemics arising from serpentine-intolerant ancestors; more productive climates may have been more suitable for the persistence of small neoendemic taxa with novel adaptations during and after speciation. Paleoendemics, on the other hand, occupy similar climates to those of their closest relatives, suggesting that range contractions leading to biotype depletion may have been similar in arid and mesic regions (Anacker, 2014). It is as of yet unclear whether climate can alter soil-specific competitiveness in edaphic endemics (see Fernandez-Going & Harrison, 2013) and whether paleoendemics and neoendemics differ in their sensitivities to competition.
Climate change will clearly have differential effects on the ranges of edaphic specialists. In California, future climate conditions may extend the potential range of many endemics (Loarie et al., 2008); however, whether edaphic endemics can naturally disperse to suitable habitat is questionable (Damschen et al., 2012; Spasojevic et al., 2014). Preadaptations to dry conditions may allow edaphic specialists to expand their current range (Femandez-Going et al, 2012; Femandez-Going, 2014) and even be more competitive with non-specialists off of their special edaphic niche (Moore et al, 2013). Tolerance of edaphic stress appears to go hand-in-hand with tolerance of climatic stress for plants growing on serpentine soils, linking soil infertility to a stress-tolerant functional trait syndrome that confers unusually high resistance to climate change upon plant species and communities (Harrison et al., 2015). Therefore, in the absence of nutrient deposition, stress-tolerant invasive species, and habitat loss, edaphic specialists may perform better under future warmer/drier climates relative to plants adapted to more fertile soils. With possible range expansions onto 'new' habitat, however, they will no longer be restricted to their special edaphic niche, thereby losing their edaphic endemic status (Anacker, 2014). Habitat patchiness may also contribute to invasiveness, with competitive and dispersal abilities evolving more rapidly on island-like habitats (Williams et al., 2016), suggesting that fragmentation can select for more rapid invasion velocity. How these findings are influenced by different climatic regimes, or by habitat patches with different levels of edaphic stress, are also important avenues for research. Naturally fragmented edaphic islands, such as serpentine outcrops, are model habitats for exploring such questions and for testing the roles of patch size, shape, type (soil), and isolation in ecological and evolutionary processes (Gil-Lopez et al., 2014).
What is the Genetic Basis of Edaphic Specialization and Speciation?
In the era of genomics, there are many tools (e.g., Bratteler et al, 2006a, b; von Wettberg & Wright, 2011; Selby et al, 2014) at our disposal to explore the genetic basis of adaptation to harsh environments, including the nature of adaptation to dissimilar habitats with similar abiotic stressors (e.g., arid and saline habitats contributing to water stress, saline and serpentine soils contributing to ionic stress, or serpentine and carbonate soils contributing to high pH). Phylogenetic analyses show that there is a significant association between halophytes and metal hyperaccumulators, although within each group there is low phylogenetic clustering (Moray et al., 2016), suggesting that salinity and metal tolerance can vary among close relatives. In Asteraceae, Amaranthaceae, Fabaceae, and Poaceae, halophytes and hyperaccumulators are more closely related than would be expected if the two traits had evolved independently, suggesting a strong genetic association between the abilities to tolerate salt and heavy metals. Studies of evolutionary ecology now routinely use high-throughput sequencing and other genomic approaches to examine the genetic basis of speciation (Tiffin & Ross-Ibarra, 2014) and these methods have clearly promoted the study of edaphic adaptation (Turner et al, 2010; Porter et al., 2017).
Genomic polymorphisms that are differentiated between edaphically contrasting populations can reveal candidate loci for edaphic adaptation. Gene pool sequencing of serpentine and granitic populations of Arabidopsis lyrata from the USA shows that the polymorphisms that are most strongly associated with soil type are loci for heavy-metal detoxification and calcium and magnesium transport, providing several candidate loci for serpentine adaptation (Turner et al., 2010), including CAX7, which appears to be responsible for adaptation to low calcium to magnesium ratios characteristic of serpentine soils (Turner et al., 2008). Moreover, the same associations between individual loci and serpentine tolerance were observed in the European subspecies of A. lyrata, further implicating edaphic selection. The sequencing of three candidate loci in the European subspecies indicated parallel differentiation of the same polymorphism at one locus, confirming edaphic specialization, and different polymorphisms at two other loci, suggesting convergent evolution. Whether these loci also contribute to reproductive isolation between progenitor-derivative taxon pairs is unknown.
Adaptation to low soil calcium to magnesium ratios has often been suggested as key to serpentine tolerance (Palm & Van Volkenburgh, 2014). In serpentine-intolerant Arabidopsis thaliana, an induced loss of function mutation in the [Ca.sup.2+]- [H.sup.+] antiporter, CAX1, enhances survival on soils with a low calcium to magnesium ratio (Bradshaw, 2005). CAX1 is a high-capacity [Ca.sup.2+]-[H.sup.+] antiporter that maintains cytoplasmic ion homeostasis by pumping excess calcium from the cytoplasm into the vacuole (Cheng et al, 2003). Mutation of CAX1 effectively acts as a magnesium exclusion strategy, enabling the plant to maintain adequate cytoplasmic calcium concentrations under the low calcium to magnesium ratios encountered on serpentine soils.
Additional candidate genes have recently been identified for serpentine adaptation in autotetraploid Arabidopsis arenosa, providing evidence that some selected alleles were introgressed from the diploid serpentine-endemic A. lyrata, whereas others were independently involved in separate adaptation events in the two species (Arnold et al, 2016). The research by Arnold et al. (2016) shows strong evidence for selection on genes that control specific ion homeostasis-related traits, as well as drought adaptation. Although several alleles under selection appear to have been introgressed from A. lyrata, others have been independently selected following serpentine colonization in both species. The significant overlap between selected genes in serpentine- endemic A. arenosa and A. lyrata suggests that adaptations to serpentine are not qualitatively different between diploid and tetraploid species. The work described above on Arabidopsis (Turner et al., 2008,2010; Arnold et al., 2016) advances our understanding of the polygenic basis of multi-trait adaptation to serpentine soils and its repeatability across species. Further, the work suggests that edaphic divergence can occur even in the presence of high levels of inter- and intraspecific gene flow. Serpentine- tolerant Arabidopsis taxa, along with their close relatives, can provide a useful system for investigating the genetics of speciation under the serpentine influence.
The genetic tools at our disposal (Sun & Schliekelman, 2011; von Wettberg & Wright, 2011; Tiffin & Ross-Ibarra, 2014) can reveal the genetic architecture of adaptive traits that confer reproductive isolation (i.especiation genes; Nosil & Schluter, 2011) and whether the same alleles or different alleles contribute to parallel evolution (Ostevik et al., 2012), revealing new insights into the mechanisms by which natural selection can bring about adaptation, reproductive isolation, and speciation. Mechanisms resulting in reproductive isolation may be incidental byproducts of natural selection on linked loci or on loci with pleiotropic effects. For example, plant populations on serpentine and other harsh edaphic settings often flower early (O'Dell & Rajakamna, 2011). Such phenological isolation could be a byproduct of adaptation to harsh soils or a result of an independent set of genetic changes that were favored by natural selection (Baack et al., 2015). A detailed genetic analysis of the alleles responsible for reproductive barriers can separate these hypotheses, particularly when traits are correlated and contribute to reproductive isolation. In Mimulus, differences in flowering time are often associated with differences in soil water availability (Wu et al., 2010; Friedman & Willis, 2013). In wet coastal and dry inland populations of Mimulus guttatus (Lowry et al., 2008), an inversion polymorphism appears to be a major quantitative trait locus (QTL) for flowering time and growth-related traits, explaining 20-30% of the variation observed between populations (Lowry & Willis, 2010). Reciprocal transplant experiments have demonstrated strong local adaptation in traits that map to the inversion and differ between the coastal and inland ecotypes (Lowry et al., 2008; Hall et al., 2010).
In Mimulus guttatus, the locus that contributes to copper tolerance also leads to hybrid lethality in crosses between copper-tolerant and -intolerant populations (Macnair & Christie, 1983). High-resolution genome mapping show that copper tolerance and hybrid lethality are not caused by the same gene, but are separately controlled by two tightly linked loci (Wright et al., 2013; Fig. lc). Selection on the copper tolerance locus indirectly causes the hybrid incompatibility allele to increase in frequency in the mine population via hitchhiking. Therefore, hybrid incompatibilities can evolve as a byproduct of an adaptation to a novel edaphic environment. Whether there are similar bases for hybrid lethality between edaphically divergent ecotypes of serpentine tolerant species such as Collinsia sparsiflora (Moyle et al., 2012; Fig. Id) remains to be seen.
Current model systems are not representative of all life history strategies and are mostly restricted to herbs, and we need to continue to add new model systems to allow comparative approaches for exploring the intricacies of adaptive evolution (Selby et al., 2014; von Wettberg et al., 2014). In this regard, the extensive work on the genetics of metal tolerance (Verbruggen et al., 2009) in metal-accumulating and hyperaccumulating plants used in phytoremediation (Rascio & Navari-Izzo, 2011), and work on the genetics of abiotic stress tolerance and phenology in crops (Roy et al., 2011), are important for examining the genetic bases for edaphic adaptation and species divergence.
Conclusions and Future Directions
Edaphic specialists are key players in the study of local adaptation and ecological speciation (Crawford et al., 2014). Ecological, physiological, phylogenetic, and population genomic studies of plants growing on serpentine, saline, and metal-contaminated soils continue to shed light on factors and mechanisms driving ecological speciation (Table 2). Studies such as those on Mimulus on copper-enriched soil (Macnair & Christie, 1983; Macnair et al., 1993; Wright et al., 2013; Fig. lc], Collinsia and Arabidopsis on serpentine soil (Moyle et al., 2012; Turner et al., 2010; Fig. Id), Helianthus on saline soils (Edelist et al, 2009; Fig. lb], and Senecio on sand dunes and rocky headland soils (Melo et al., 2014), are key to establishing a direct link between adaptation, reproductive isolation, and subsequent speciation. Ongoing research on Mimulus, Helianthus, and Arabidopsis (and others; Tables 1 and 2) will continue to unravel how edaphic conditions can directly or indirectly contribute to species divergence.
Lessons on Evolution
There are several key lessons on evolutionary processes from the study of edaphic specialization:
a. Both adaptive phenotypic plasticity and local adaptation contribute to edaphic divergence. Edaphic specialization is key to diversification in some groups; however, in others, there appears to be lack of variation for adaptation to harsh soils. Although edaphic specialization is important in the diversification of flowering plants and ferns, there is little evidence for its significance in other plant groups such as gymnosperms and bryophytes or in lichens, soil algae, and cyanoprokaryotes.
b. Although edaphic specialists can evolve under allopatric, parapatric, and sympatric modes of speciation, there is strong evidence pointing to budding or peripatric speciation being central to the origin of neoendemic species (Anacker & Strauss, 2014). Additionally, an increasing body of work shows that speciation is possible in the face of gene flow, especially in lineages where there is considerable ecological (including edaphic) divergence. Further, introgression between close relatives can also lead to the acquisition of edaphic tolerance (Arnold et al., 2016).
c. Edaphic adaptations have direct or indirect effects on reproductive isolation; adaptive and reproductively isolating traits can evolve rapidly and repeatedly in some lineages, making edaphic specialists key to studying parallel speciation.
d. There is mixed evidence for a physiological cost of edaphic tolerance driving habitat specialization, although both reduced competitive ability and greater susceptibility to herbivory have been documented among some edaphic specialists when grown in 'normal' soils.
e. Mutualistic and antagonistic interactions with other organisms can mediate edaphic specialization either by directly enhancing tolerance to edaphic extremes via the action of microbes or by reducing gene flow between divergent populations via the action of pollinators, herbivores, and pathogens.
f. Climate and soils can interact to influence edaphic specialization. Future climates may further restrict the distribution of edaphic specialists due to increased competition from invasive species. However, edaphic specialists could also expand their ranges, even outside their edaphic niche, if their preadaptations to drought make them more competitive than non-specialists under a drying climate.
g. QTL mapping studies, population genomic approaches, and high-throughput phenotyping assays, when combined with reciprocal transplant studies using hybrid mapping populations (including, F2, backcross, near isogenic lines, and recombinant inbred lines), can identify major loci contributing to edaphic adaptation to serpentine, saline, and heavy metal-rich soils (Selby et al., 2014). These loci often have direct or indirect effects on loci that contribute to reproductive isolation (Table 2).
Information Gaps and Future Directions
There are several information gaps that need to be addressed to better develop current model systems as well as to incorporate additional taxa for the study of edaphic specialization. The following are key areas for future research:
a. The identification of specific soil factors that are central to edaphic specialization is important for demonstrating the role of adaptation in speciation. Although most studies state only the general soil type (e.g., serpentine versus non- serpentine, saline versus non-saline, gypsum versus non-gypsum, etc.) being investigated, a handful of studies have attempted to examine the exact soil chemical or physical factor contributing to the specialization and/or divergence (Rajakaruna et al., 2003a, b; Bradshaw, 2005; Bratteler et al., 2006, b; Palacio et al., 2007; Edelist et al., 2009; Selby et al., 2014). Identifying the key soil variable or variables is more effective when comparing sister populations found across substrates that differ in a distinct way (e.g., with or without a heavy metal as in the case of copper tolerance in Mimulus). Plant ionomic approaches can also be used to investigate ecological functions of ionomic alleles in the adaptation to distinct soils (Lowry et al., 2012; Huang & Salt, 2016).
b. Better characterization of functional traits (e.g., morphological, physiological, and reproductive traits) between sister species that differ in their edaphic niche is also critical for determining which traits may be contributing to the divergence. Whether traits characteristic of the edaphic habitat are plastic responses or are genetically based should also be confirmed. Once those traits targeted by edaphic selection are identified, the physiological/genetic basis of those traits should be determined. Much of what we know about edaphic specialization comes from studies on plants found on metal mines, serpentine soils, or saline environments of temperate or Mediterranean climes, and it is essential that we expand our studies to identify and characterize systems found on other types of substrates and in other climatic regions of the world. Such a broad survey can reveal similarities and differences in trends associated with speciation resulting from edaphic specialization.
c. Because multiple reproductive barriers can contribute to reduced gene flow between divergent taxa (Baack et al., 2015; Ostevik et ah, 2016), it is important to identify and characterize the relative contribution of all pre- and post- zygotic reproductive isolating mechanisms to the total reproductive isolation between edaphically divergent pairs. The order in which barriers originate and their genetic bases and associations with traits characterizing edaphic adaptations may shed light on the relative importance of each barrier to different stages of a divergence event and at different levels of habitat specialization.
d. Why edaphic tolerance only sometimes leads to speciation is still unknown. It is possible that speciation is more likely when an adaptation or a suite of adaptations comes with a large fitness trade-off between edaphic habitats, contributing to stronger divergent selection across edaphic boundaries. A greater cost of tolerance may lead to adaptations that have a direct or indirect effect on reproductive isolation, leading to the evolution of endemic species. This fundamental gap in our understanding of edaphic specialization can be answered by using multiple, progenitor-derivative taxon pairs that have adaptively diverged along the same edaphic axis but which vary in their accommodation to the substrate (i.e., tolerator versus endemic). Field surveys to characterize the habitat differences (i.e., are endemics found on harsher soils than tolerator species?), reciprocal transplant studies to estimate the fitness trade-offs (i.e., is there a greater cost of tolerance in species pairs with endemics relative to those with tolerators?), and greenhouse studies to assess the extent of reproductive isolation between pairs (i.e., is there greater reproductive isolation in species pairs with endemics relative to those with tolerators) can reveal answers to this critical question.
e. Edaphic specialists offer opportunities, via methods of comparative genomic and population genetic analyses, to examine the relationships among genetic loci that are responsible for adaptations and the degree to which they influence reproductive isolation (Crawford et al, 2014). In addition to the elegant work done on model plants such as Helianthus (Andrew & Rieseberg, 2013), Mimulus (Selby et al., 2014), and Arabidopsis (Turner et al., 2008, 2010; Arnold et al, 2016), the genetic architecture of traits conferring adaptation and reproductive isolation should be explored in other species with good ecological and biological data supporting edaphic differentiation. Serpentine-tolerant plants such as Silene (Bratteler et al., 2006, b), Lasthenia (Rajakaruna, 2003), Layia (Baldwin, 2005), Leptosiphon (Kay et al., 2011), Streptanthus (Pope et al., 2014), and Collinsia (Moyle et al., 2012); metal-tolerant plants including Alyssum, Caulanthus, and Thalspi (Noccaea) (Mengoni et al., 2003a, b; Burrell et al., 2012; Gill et al., 2012); selenium-tolerant plants such as Stanleya and Astragalus (Schiavon & Pilon-Smits, 2017); and gypsophiles such as Mentzelia, Nama, and Helianthemum (Moore et al., 2014 and references therein) are ideal for testing how findings from the model plants may be applicable across a wider range of wild plants experiencing a broader array of edaphic pressures. Taxa within these genera show a range of divergence stages and degrees of edaphic endemism and, in many cases, their natural history and ecology are well documented via both descriptive and experimental methods. For some of these taxa (or their close relatives), there are extensive genetic tools already in place. Genome scans, when combined with candidate gene approaches, comparative transcriptomics, QTL mapping, functional analysis, and experimental manipulation, can reveal loci with high levels of differentiation between edaphically divergent populations, enabling the discovery of genes driving adaptation and reproductive isolation (Selby et al., 2014; Faria et al., 2014; Floban et al, 2016). In species for which there is evidence for parallel evolution of traits, it will be critical to test whether the same or different alleles are responsible for the parallel speciation events (Ostevik et al., 2012; Roda et al., 2013).
f. Edaphic specialists can help determine how prezygotic and postzygotic reproductive isolating mechanisms limit gene flow between close relatives at various geographical scales. The often widely disjunct and patchy distribution patterns of edaphic specialists provide settings in which to test whether pre-zygotic isolating mechanisms are stronger in populations in parapatry/sympatry relative to those in allopatry. Enhanced reproductive isolation between edaphically divergent taxa found under parapatiy/sympatiy, relative to those in allopatry, may reflect the action of reinforcement, i.e., selection for reduced gene flow to avoid maladaptive hybridization (Widmer et al., 2009). There are only a few well- documented cases of reinforcement in plants (Baack et al., 2015) and edaphic specialists may provide good model systems for testing the importance of this process in plant speciation (see Silvertown et al., 2005).
g. Comparative genomic and population genetic analyses can reveal how habitat specialization is achieved and maintained in the face of gene flow (Papadopulos et al., 2011). Hybridization and polyploidization are ubiquitous forces in the diversification of plants, and edaphic endemic species can help reveal how these two forces influence divergence (Kane, 2009).
h. Chromosomal rearrangements can contribute to reproductive isolation through their effects on hybrid fertility, as well as by reducing interspecific recombination and gene flow (Baack et al., 2015). In Mimulus, a chromosomal inversion polymorphism contributes to differences in flowering time and other traits, as well as multiple reproductive barriers between annual and perennial ecotypes of M. guttatus (Lowry & Willis, 2010). Whether karyological anomalies drive isolation between edaphically divergent individuals must be tested on species pairs showing post-mating and post-zygotic isolation.
i. If soil elements, like heavy metals, have a direct impact on reproductive isolation of edaphically divergent taxa, it is easy to demonstrate that adaptation to a specific soil factor can directly contribute to isolation and subsequent divergence. The work exploring how heavy metal accumulation in reproductive tissue can influence reproductive success (Searcy & MacNair, 1993; Quinn et al., 2011a), including pollinator-mediated isolation (Meindl & Ashman, 2013, 2014, 2015), is important for further exploration, especially in sister taxa in which one taxon is a metal hyperaccumulator.
j. Metal hyperaccumulators have received much attention as candidates for green technologies such as phytoremediation and phytomining (Rascio & Navari-Izzo, 2011). However, they also provide opportunities for exploring the cost of edaphic tolerance hypothesis on habitat specialization. In genera with metal-tolerant, metal-hyperaccumulating, and metal-intolerant species (such as in Alyssum, Thlaspi/Noccaea, Streptanthus, and Silene), sister taxa can be used to test whether there is a trade-off in terms of competitive ability between metal-intolerant versus metal-tolerant and metal-intolerant versus metal hyperaccumulator sisters (prediction: greater trade-off in the metal-intolerant versus metal-hyperaccumulator pair). Further, to explore if the cost of tolerance to edaphic specialization drives speciation, one could test whether there is a greater trade-off between metal-intolerant versus edaphic endemic metal hyperaccumulator pairs or metal-intolerant versus nonendemic metal hyperaccumulator pairs (prediction: greater trade-off in competitive ability in the metal intolerant versus edaphic endemic metal hyperaccumulator pair).
k. Plants found in stressful environments tend to share a suite of traits (i.e., stress resistance syndrome or SRS traits) that provides cross-tolerance to a range of low productivity habitats (Brady et al., 2005; von Wettberg et al., 2014 and references therein). It is unclear if the same SRS loci or different loci are responsible for edaphic shifts seen across distinct substrates (e.g between serpentine and limestone, serpentine and saline, serpentine and mine tailing, limestone and dolomite/gypsum, etc.) characterized by overlapping selection pressures (e.g., drought, pH, ionic strength, ions, etc.). If SRS traits are shared (with or without a similar genetic basis), one can envision how an adaptation to one 'harsh' soil type can preadapt a lineage to another 'harsh' soil type. In Mimulus, Arabidopsis, Helianthus, and others such as Lasthenia (Rajakaruna, 2003), Silene (Mengoni et al., 2001), and Minuartia (Moore & Kadereit, 2013) there are multiple species showing adaptation to numerous soil types, including those characterized by similar selection pressures: ions, pH, drought, etc. Ecological, phylogenomic, and population genomic studies of plants showing such cross-tolerance to distinct soil types can provide insights on common physiological traits and trends associated with edaphic specialization.
l. Climate change is clearly a major stressor influencing plant diversity. How edaphic specialists will respond to climate change may depend on whether they are preadapted to future climate conditions, cross-tolerant to edaphic-climatic stressors (e.g., salt-drought), can compete under novel climates, or can rapidly evolve climate tolerance, as well as how quickly, how far, and how effectively they can disperse into suitable edaphic niches under a changing climate (Fernandez-Going, 2014). Further, how cross kingdom interactions (both mutualistic and antagonistic) might play into these possible outcomes is unknown. Studies of the interaction between climate and edaphic factors in determining the distribution of edaphic specialists should incorporate species from multiple lineages, growth forms, substrate types, and varying climates to gain a better understanding of how climate-associated threats will impact edaphically specialized plants.
The study of edaphic specialization continues to provide unique perspectives on the processes of evolution and will continue to lead the way in understanding the important role ecology plays in the origin of species and assembly of special plant communities. The fast-growing field of molecular ecology will undoubtedly play a key role in this regard, especially by aiding in the discovery of genes responsible for adaptation and reproductive isolation under edaphic influences. Edaphically specialized plants will also provide model systems for exploring little-studied phenomena in plant evolution such as the importance of reinforcement of reproductive isolation in speciation and the nature of parallel speciation. Lastly, research on edaphic specialization, particularly the study of adaptation to edaphic factors such as nutrient levels, salt, heavy metals, and drought, will help counter growing challenges faced in fields such as agriculture (Rozema & Schat, 2013) and habitat restoration (O'Dell, 2014), and contribute to advancing green technologies, including phytoremediation and phytomining (Chaney et al., 2014).
Acknowledgments I would like to thank Bob Boyd, Ian Medeiros. Elizabeth Farnsworth, Susan Harrison, Tanner Harris, and Jonathan Gressel for constructive comments on earlier drafts of the manuscript Additional comments from Mark R. Macnair and an anonymous reviewer greatly improved the manuscript. Funding from the US-Sri Lanka Fulbright Commission during the writing of this review is gratefully acknowledged.
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Nishanta Rajakaruna (1,2,3)
(1) Biological Sciences Department, California Polytechnic State University, San Luis Obispo, CA 93407, USA
(2) Unit for Environmental Sciences and Management, North-West University, Private Bag X6001, Potchcfstroom 2520, South Africa
(3) Author for Correspondence; e-mail: email@example.com Published online: 26 October 2017
Caption: Fig. 1 Examples of edaphic influence on speciation and reproductive isolation. A Howea foresteriana is largely restricted to limestone, while H. belmoreana is largely restricted to basalt (Savolainen et al., 2006; Hipperson et al., 2016). Their geographic separation is accompanied by reproductive isolation via a difference in flowering time: peak flowering in H. foresteriana (H. f.) occurs around two months before H. belmoreana (H. b). B Helianthus annuus (H. a.) and H. petiolaris are salt-intolerant species (glycophytes), but H. paradoxus (H. pa.), which originated as a hybrid between the former two species, is a halophyte (Lexer et al., 2003; 2004). Genetic studies suggest that this may be due to changes in the expression of genes for ion transporters, with increased calcium uptake limiting sodium uptake in the halophyte (Edelist et al., 2009). C Mimulus guttatus has both copper-tolerant and -intolerant populations in California. The alleles for copper tolerance (Toll) and hybrid lethality (Ned) are at closely linked genetic loci; as selection for copper tolerance occurred, both alleles rose to high frequency in the population on copper- contaminated soil (Wright et al., 2013). D Collinsia sparsiflora has serpentine and nonserpentinc ecotypes. Progeny of within-ecotype crosses have high fertility; between-ecotype hybrids do occur, but the genetic distance between the ecotypes is maintained because these hybrids have reduced fertility (ca. 26% reduction in seed viability in FI; Moyle et al., 2012). Image Credit: Ian D. Medeiros
Table 1 Proposed modes of speciation and substrate type for some taxa having presumably diversified under edaphic selection Species Mode of Speciation Type of Substrate Adi an turn Hybrid, Polyploid Serpentine viridimontanum Arabidopsis spp. Hybrid Serpentine Arctostaphylos spp. Hybrid Serpentine Armeria spp. Hybrid Serpentine Caulanthus amplexicaulis Allopatric Serpentine var. barbarae Galium spp. Hybrid Serpentine Geonoma macrostachys Sympatric Terra finne and moist flood plain Harmonia spp. Allopatric Serpentine Helianthus spp. Hybrid, Polyploid, Desert, Sand Dune. Peripatric Salt Marshes Hesperolinon spp. Peripatric Serpentine Howea spp. Sympatric Volcanic and carbonate Iris spp. Hybrid Flooded soils Knautia arvensis Allopatric Serpentine Knautia spp. Hybrid/Polyploid Serpentine Lasthenia califomica Allopatric Ionically-harsh complex soils such as saline, serpentine, etc. Layia disc odea Parapatric. Serpentine Peripatric Leptosiphon parviflorus Parapatric Serpentine Mentzelia monoensis Peripatric Silica-rich rhyolite tephra Metal-tolerant grasses Peripatric Metal mines Mimulus spp. Peripatric Saline. Serpentine, Dry/Wet Minuartia laricifolia Allopatric Serpentine subsp. ophiolitica Potentilla spp. Hybrid Serpentine Protium spp. Parapatric White-Sand Quercus spp. Hybrid Serpentine Silene dioica Allopatric Serpentine Streptanthus glandulosus Allopatric Serpentine complex Species Reference Adi an turn Paris & Windham, 1988; viridimontanum Paris, 1991 Arabidopsis spp. Arnold et al., 2016 Arctostaphylos spp. Gottlieb, 1968 Armeria spp. Feliner et al., 1996 Caulanthus amplexicaulis Pepper & Norwood, 2001 var. barbarae Galium spp. Krahulcova & Stepankova, 1998 Geonoma macrostachys Borchsenius et al., 2016 Harmonia spp. Baldwin, 1999 Helianthus spp. Lai et al, 2005; Yakimowski & Ricseberg, 2014 and references therein Hesperolinon spp. Schneider et al., 2016 Howea spp. Savolaincn et al., 2006 Iris spp. Martin et al., 2006 Knautia arvensis Kaplan, 1998 Knautia spp. Kolar et al., 2014 Lasthenia califomica Rajakaruna, 2003; complex Kay et al., 2011 Layia disc odea Baldwin, 2005 Leptosiphon parviflorus Kay et al., 2011 Mentzelia monoensis Brokaw et al., 2015 Metal-tolerant grasses Antonovics, 2006 Mimulus spp. Grosscnbacher et al., 2014; Selby et al., 2014; Sobel, '2014 Minuartia laricifolia Moore et al., 2013 subsp. ophiolitica Potentilla spp. Paule et al., 2015 Protium spp. Fine et al., 2013 and references therein Quercus spp. Forde & Faris, 1962 Silene dioica Westerbergh & Saura, 1992 Streptanthus glandulosus Mayer & Soltis, 1994, 1999 complex Table 2 Some case studies of edaphic differentiation where soil type shifts between close relatives (sister taxa, congeners, populations) have been confirmed via ecological, physiological, phylogenetic, or population genetic studies. Traits identified via experimental studies as key to adaptation and reproductive isolation are listed along with any direct evidence for their genetic bases. For a detailed list of adaptive and reproductive trait differences between close relatives found on and off serpentine soils see O'Dell and Rajakaruna (2011). Unknown=results inconclusive, no evidence, or not studied Species Soil Type Agrostis tenuis, A. Zinc and Copper mine soil (Wu et al., capillaris, 1975; Nichols & McNcilly, 1982; and A. stolonifera Al-Hiyali ct ah, 1993); Saline soil (Venables & Wilkins, 1978) Alyssum serpyllifolium Serpentine (Sobczyk ct ah, 2017) Anthoxanthum odoratum Mine soil. Park Grass Experiment (nutrient and lime treatments) (Silvcrtown et ah, 2005; Antonovics, 2006) Arabidopsis halleri Metal soils (Hunter & Bomblies, 2010) Arabidopsis lyrata Serpentine (Turner ct ah, 2008) Anneria maritima Calamine soils (Baumbach & Hellwig, 2007) Caulanthus amplexicaulis Serpentine (Pepper & Norwood, 2001) var. barbarae Ceanothus roderickii Gabbro (Bulge & Manos, 2011) Cerastium alpinum Serpentine (Nybcrg Bcrglund ct al., 2004) Collinsia sparsiflora Serpentine (Moyle ct al., 2012) Deschampsia cespitosa Metal soils (Hayward ct al., 2013) Geonoma macrostachys Well-drained vs poorly-drained soil (Borchsenius et al., 2016) Helianthemum spp. Gypsum (Moore ct al., 2014) Helianthus exilis Serpentine (Sambatti & Rice, 2007) Helianthus paradoxus Salt (Lexer et al., 2003) Howea forsteriana and Volcanic soil and calcareous soil H. belmoreana (Savolaincn ct a!., 2006) Lasthenia califomica Serpentine/Saline/Dry (Rajakaruna complex et al., 2003a, b) Lasthenia maritima Guano (Crawford et al., 1985) Layia discoidea Serpentine (Baldwin. 2005) Leptosiphon parviflorus Serpentine (Kay et al., 2011) Mimulus guttatus Dry (inland)/Wet (coastal) (Lowry et al., 2009) Mimulus guttatus, Serpentine (Selby et al, 2014) M. congdonii, M. douglasii. M. Jloribundus, M. glaucescens, M. kelogii, M. layneae, M. mephiticus, M. nudatus, M. pardalis Mimulus guttatus. Copper (Macnair & Christie, 1983; M. cupriphilus Wright et al., 2013) Mimulus laciniatus Granite (Peterson et al., 2013) Noccaea caerulescens Serpentine and other metal-enriched soils (Mandakova et al., 2015) Senecio lautus Sandy dunes and rocky headlands (Melo et al., 2014) Silene vulgaris Serpentine (Bratteler et al., 2006, b); Copper soils (van Hoof et al., 2001) Species Adaptive Traits Agrostis tenuis, A. Multiple mechanisms, including capillaris, nicotianamine, L-cystcine, and A. stolonifera superoxidc dismutase production, and HSP70 overexpression (Hego et al., 2016) Alyssum serpyllifolium Nickel hyperaccumulation (Sobczyk et al., 2017) Anthoxanthum odoratum Metal exclusion from shoot (Qurcshi et al., 1985); nitrogen tolerance (Freeland et ah, 2010) Arabidopsis halleri Zinc and Cadmium tolerance (Roux et al., 2011) Arabidopsis lyrata Possibly, heavy metal and Ca:Mg tolerance (Turner et ah, 2008, 2010) Anneria maritima Role of malatc in metal translocation, reduced oxidative stress (Olko et al., 2008; Parys et ah, 2014) Caulanthus amplexicaulis Nickel tolerance (Burrell ct ah, 2012) var. barbarae Ceanothus roderickii Low nutrient and Ca:Mg tolerance (Burge & Manos, 2011) Cerastium alpinum Magnesium and nickel tolerance (Nyberg Bcrglund ct al., 2004) Collinsia sparsiflora Possibly, Ca:Mg tolerance (Moyle et al., 2012) Deschampsia cespitosa Increased nicotianaminc and phytochclatin synthesis (Hayward et al., 2013) Geonoma macrostachys Unknown Helianthemum spp. Accumulate excess calcium as oxalate (Palacio et al., 2014): sulphate accumulation (Moore et al., 2014) Helianthus exilis Magnesium and sodium exclusion, water use efficiency (Sambatti & Rice. 2007) Helianthus paradoxus Increased calcium, potassium uptake and sodium exclusion (Lexer ct al., 2003. 2004; Edelist et al., 2009) Howea forsteriana and Tolerance to salinity, drought, pH H. belmoreana (Dunning et al., 2016) Lasthenia califomica Enhanced shoot magnesium and complex sodium tolerance (Rajakaruna et al., 2003a); Early and increased flowering under drought (Rajakaruna et al., 2003b) Lasthenia maritima Elevated leaf nitrogen levels (Omduff, 1965)-exact mechanism of tolerance Unknown Layia discoidea Unknown Leptosiphon parviflorus Unknown Mimulus guttatus Elevated leaf sodium levels (Lowiy et al., 2009)--exact mechanism of tolerance unknown Mimulus guttatus, Tolerance to low soil Ca:Mg and high M. congdonii, nickel; Greater magnesium M. douglasii. accumulation in shoot (Selby et al., M. Jloribundus, 2014; Palm et al., 2012) M. glaucescens, M. kelogii, M. layneae, M. mephiticus, M. nudatus, M. pardalis Mimulus guttatus. Copper tolerance (Macnair, 1983; M. cupriphilus Macnair et al., 1993; Smith & Macnair. 1998) Mimulus laciniatus Drought tolerance (Peterson et al., 2013) Noccaea caerulescens Enhanced metal homeostasis gene expression (Mandakova et al., 2015) Senecio lautus Salinity tolerance, potassium transport (Roda et al., 2013) Silene vulgaris Nickel tolerance (Brattclcr et al., 2006); Copper tolerance (van Hoof et al., 2001) Species Reproductive Barriers Agrostis tenuis, A. Unknown capillaris, and A. stolonifera Alyssum serpyllifolium Unknown Anthoxanthum odoratum Flowering time difference; self-fertility (Antonovics, 1968, 2006; Silvertown et ah, 2005) Arabidopsis halleri Reduced hybrid fitness (Hunter & Bomblies, 2010) Arabidopsis lyrata Genetic variation for flowering time (Hunter & Bomblies, 2010) Anneria maritima Partial self-fertility (Vckemans & Lefebvre, 1997) Caulanthus amplexicaulis Unknown; possibly, geographic var. barbarae isolation via biotype depletion as it is completely interfertile in artificial crosses with sister taxon (Pepper & Norwood, 2001) Ceanothus roderickii Selection against hybrids in parental habitats and possible genetic incompatibilities (Burge ct al., 2013) Cerastium alpinum Unknown; possibly, selection against hybrids (Ostevik et al., 2012) Collinsia sparsiflora FI hybrid sterility (Moyle ct al., 2012) Deschampsia cespitosa Unknown Geonoma macrostachys Flowering time and pollinators (Borchsenius ct al., 2016) Helianthemum spp. Unknown Helianthus exilis Unknown Helianthus paradoxus Habitat segregation due to salt tolerance; differences in photoperiodicity; hybrid sterility (Lai et al., 2005; Henry et al., 2014; Palacio ct al., 2014) Flowering time differences and selection against hybrids Howea forsteriana and (Savolainen et al., 2006; Hipperson H. belmoreana et al., 2016) Lasthenia califomica Flowering times, pollen-stigma complex incompatibilities (Rajakaruna & Whitton, 2004) Lasthenia maritima Self-compatibility (Crawford ct al., 1985) Layia discoidea Unknown; possibly selection against hybrids in parental habitats Leptosiphon parviflorus Flowering time difference, possibly, flower color (Kay et al., 2011) Mimulus guttatus Flowering time (Lowry & Willis, 2010) Mimulus guttatus, Self-compatibility, Flowering times, M. congdonii, hybrid lethality, pollinator M. douglasii. differences (Gardner & Macnair, M. Jloribundus, 2000; Selby et al., 2014) M. glaucescens, M. kelogii, M. layneae, M. mephiticus, M. nudatus, M. pardalis Mimulus guttatus. Self-compatibility, flowering time M. cupriphilus differences, hybrid lethality (Christie & Macnair, 1984, 1987; Macnair et al., 1989; Friedman & Willis, 2013; Wright et al., 2013) Mimulus laciniatus Flowering time differences (Ferris et al., 2016) Noccaea caerulescens Possible role of inversion polymorphism (Mandakova et al., 2015); lower selling rates in metallicolous populations (Dubois et al., 2003; Mousset et al., 2016) Senecio lautus Immigrant inviability and extrinsic postzygotic isolation via herbivores and soil type (Melo et al., 2014 Silene vulgaris Unknown Species Spcciation Genes Agrostis tenuis, A. Unknown capillaris, and A. stolonifera Alyssum serpyllifolium Unknown Anthoxanthum odoratum Unknown Arabidopsis halleri Unknown; HMA4 (heavy metal ATPase 4) provides metal tolerance (Roux et ah, 2011) Arabidopsis lyrata Unknown; QTL associations between local adaptation and flowering time (Lcinonen et al., 2013) Anneria maritima Unknown Caulanthus amplexicaulis Unknown var. barbarae Ceanothus roderickii Unknown Cerastium alpinum Unknown Collinsia sparsiflora Unknown Deschampsia cespitosa Unknown Geonoma macrostachys Unknown Helianthemum spp. Unknown; phylogeny available (Parejo-Fames et al., 2013) Helianthus exilis Unknown Helianthus paradoxus Karyotypic differences leading to hybrid sterility (Lai et al., 2005) Plciotropy or linkage between loci contributing to flowering Howea forsteriana and time and adaptation to water, H. belmoreana salt, and pH stress (Dunning et al., 2016) Lasthenia califomica Unknown complex Lasthenia maritima Unknown Layia discoidea Unknown Leptosiphon parviflorus Unknown Mimulus guttatus Salt tolerance loci and an inversion locus show fitness effects in contrasting habitats; colocalization of loci for molybdenum and cadmium accumulation (Lowry & Willis, 2010; Lowry et al., 2012; Twyford & Friedman, 2015) Mimulus guttatus, Unknown M. congdonii, M. douglasii. M. Jloribundus, M. glaucescens, M. kelogii, M. layneae, M. mephiticus, M. nudatus, M. pardalis Mimulus guttatus. Linkage between Copper M. cupriphilus tolerance locus and hybrid incompatibility locus (Wright et al., 2013; also see Christie & Macnair, 1987) Mimulus laciniatus Unknown Noccaea caerulescens Possible role of metal ion homeostasis genes and chromosomal rearrangements (Mandakova et al., 2015) Senecio lautus Unknown; however, loci for ion homeostasis and reproduction are known (Roda et al., 2013) Silene vulgaris Unknown: however, constitutively higher SvMT2b expression increases the level of tolerance produced by one or more cpistatic primary tolerance genes (van Hoof et al., 2001)
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|Publication:||The Botanical Review|
|Date:||Mar 1, 2018|
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