Abstract:Both ecological and evolutionary processes can influence community assembly and stability, and native community members may respond both ecologically and evolutionarily as additional species enter established communities. Biological invasions provide a unique opportunity to examine these responses of native community members to novel species additions. Here, I use reciprocal transplant experiments among naturally invaded and uninvaded environments, along with experimental removals of exotic species, to determi… Show more
“…For example, the catastrophic effects of global warming on coral reef communities are greatly diminished when corals are colonized by particular clades of thermal-tolerant zooxanthellae symbionts (22). Second, tradeoffs between traits mediating biotic interactions and traits underlying adaptation to global change may hinder (or in some cases facilitate) evolutionary responses (23,24). For example, insect herbivores appear to inhibit adaptive responses of native plants to biological invasions, likely because of genetic tradeoffs between traits mediating interactions with herbivores and exotic plant competitors (23,24).…”
mentioning
confidence: 99%
“…Second, tradeoffs between traits mediating biotic interactions and traits underlying adaptation to global change may hinder (or in some cases facilitate) evolutionary responses (23,24). For example, insect herbivores appear to inhibit adaptive responses of native plants to biological invasions, likely because of genetic tradeoffs between traits mediating interactions with herbivores and exotic plant competitors (23,24). These complex species interactions in natural communities can make the evolutionary consequences of global change difficult to predict, but understanding adaptation in a community context is necessary for assessing species' responses to global change and identifying factors that contribute to adaptive responses to novel environments.…”
Global change is challenging plant and animal populations with novel environmental conditions, including increased atmospheric CO2 concentrations, warmer temperatures, and altered precipitation regimes. In some cases, contemporary or “rapid” evolution can ameliorate the effects of global change. However, the direction and magnitude of evolutionary responses may be contingent upon interactions with other community members that also are experiencing novel environmental conditions. Here, we examine plant adaptation to drought stress in a multigeneration experiment that manipulated aboveground–belowground feedbacks between plants and soil microbial communities. Although drought stress reduced plant growth and accelerated plant phenologies, surprisingly, plant evolutionary responses to drought were relatively weak. In contrast, plant fitness in both drought and nondrought environments was linked strongly to the rapid responses of soil microbial community structure to moisture manipulations. Specifically, plants were most fit when their contemporary environmental conditions (wet vs. dry soil) matched the historical environmental conditions (wet vs. dry soil) of their associated microbial community. Together, our findings suggest that, when faced with environmental change, plants may not be limited to “adapt or migrate” strategies; instead, they also may benefit from association with interacting species, especially diverse soil microbial communities, that respond rapidly to environmental change.
“…For example, the catastrophic effects of global warming on coral reef communities are greatly diminished when corals are colonized by particular clades of thermal-tolerant zooxanthellae symbionts (22). Second, tradeoffs between traits mediating biotic interactions and traits underlying adaptation to global change may hinder (or in some cases facilitate) evolutionary responses (23,24). For example, insect herbivores appear to inhibit adaptive responses of native plants to biological invasions, likely because of genetic tradeoffs between traits mediating interactions with herbivores and exotic plant competitors (23,24).…”
mentioning
confidence: 99%
“…Second, tradeoffs between traits mediating biotic interactions and traits underlying adaptation to global change may hinder (or in some cases facilitate) evolutionary responses (23,24). For example, insect herbivores appear to inhibit adaptive responses of native plants to biological invasions, likely because of genetic tradeoffs between traits mediating interactions with herbivores and exotic plant competitors (23,24). These complex species interactions in natural communities can make the evolutionary consequences of global change difficult to predict, but understanding adaptation in a community context is necessary for assessing species' responses to global change and identifying factors that contribute to adaptive responses to novel environments.…”
Global change is challenging plant and animal populations with novel environmental conditions, including increased atmospheric CO2 concentrations, warmer temperatures, and altered precipitation regimes. In some cases, contemporary or “rapid” evolution can ameliorate the effects of global change. However, the direction and magnitude of evolutionary responses may be contingent upon interactions with other community members that also are experiencing novel environmental conditions. Here, we examine plant adaptation to drought stress in a multigeneration experiment that manipulated aboveground–belowground feedbacks between plants and soil microbial communities. Although drought stress reduced plant growth and accelerated plant phenologies, surprisingly, plant evolutionary responses to drought were relatively weak. In contrast, plant fitness in both drought and nondrought environments was linked strongly to the rapid responses of soil microbial community structure to moisture manipulations. Specifically, plants were most fit when their contemporary environmental conditions (wet vs. dry soil) matched the historical environmental conditions (wet vs. dry soil) of their associated microbial community. Together, our findings suggest that, when faced with environmental change, plants may not be limited to “adapt or migrate” strategies; instead, they also may benefit from association with interacting species, especially diverse soil microbial communities, that respond rapidly to environmental change.
“…For example, Chew (1979) speculated that the selective pressures on the Brassicaceous host plants she studied would likely differ following invasion by the exotic crucifer Thlaspi. Several other examples of invasive plants that apparently alter attack on natives have recently emerged (Zimmerman 1960;Thomas et al 1987;Carroll and Boyd 1992;Solarz and Newman 1996;Rand and Louda 2004;Lau and Strauss 2005;Russell and Louda 2005;Lau 2006). We believe that the study of plant-herbivore interactions in both invaded versus non-invaded sites and in introduced versus native habitats are "natural experiments" that provide interesting research opportunities.…”
Section: Plant Invasions and Community Heterogeneitymentioning
“…Most studies addressing plant local adaptation have focused on the relative importance of gene Xow and natural selection (Slatkin 1973;Linhart and Grant 1996), and on the role of abiotic factors (e.g., wind, elevation, soil) as forces promoting local adaptation (Jain and Bradshaw 1966;Galen et al 1991). Except for a few studies involving competition (McGraw and Chapin 1989;Prati and Schmid 2000) and leaf herbivores (Schemske 1984;Sork et al 1993;Lau 2006), the inXuence of biotic interactions on plant local adaptation generally has been overlooked (although for animals this has not been the case; see Fauth 1998 and references therein for examples on competitive interactions and local adaptation in amphibians).…”
Few previous studies have assessed the role of herbivores and the third trophic level in the evolution of local adaptation in plants. The overall objectives of this study were to determine (1) whether local adaptation is present in the ant-defended plant, Chamaecrista fasciculata, and (2) the contribution of ant-plant-herbivore interactions and soil source to such adaptation. We used three C. fasciculata populations and performed both a field and a greenhouse experiment. The first involved reciprocally transplanting C. fasciculata seedlings from each population-source to each site, and subsequently applying one of three treatments to one-third of the seedlings of each population-source at each site: control, reduced ant density and reduced folivory. The greenhouse experiment involved reciprocal transplants of population-sources with soil sources to test for a soil-source effect on flower production and local adaptation to soil conditions. Field results showed that ant and herbivore treatments reduced ant density (increasing folivory) and herbivore damage relative to controls, respectively; however, these manipulations did not impact C. fasciculata reproduction or the likelihood of survival. In contrast, greenhouse results showed that soil source significantly affected flower production. Overall, plants in both experiments, regardless of population-source, always had higher reproductive output at one specific site. Native populations did not outperform nonnative ones, causing us to reject the hypothesis of local adaptation. The absence of treatment effects on plant reproduction and the likelihood of survival suggest a limited effect of ants and folivores on C. fasciculata fitness and local adaptation during the study year. Temporally inconsistent effects of biotic forces across years, coupled with the young age of populations, relative proximity of populations and possible counter effects of seed predators may reduce the likelihood of local adaptation in the populations studied.
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