CO2 studies remain key to understanding a future world

Summary Characterizing plant responses to past, present and future changes in atmospheric carbon dioxide concentration ([CO2]) is critical for understanding and predicting the consequences of global change over evolutionary and ecological timescales. Previous CO2 studies have provided great insights into the effects of rising [CO2] on leaf-level gas exchange, carbohydrate dynamics and plant growth. However, scaling CO2 effects across biological levels, especially in field settings, has proved challenging. Moreover, many questions remain about the fundamental molecular mechanisms driving plant responses to [CO2] and other global change factors. Here we discuss three examples of topics in which significant questions in CO2 research remain unresolved: (1) mechanisms of CO2 effects on plant developmental transitions; (2) implications of rising [CO2] for integrated plant–water dynamics and drought tolerance; and (3) CO2 effects on symbiotic interactions and eco-evolutionary feedbacks. Addressing these and other key questions in CO2 research will require collaborations across scientific disciplines and new approaches that link molecular mechanisms to complex physiological and ecological interactions across spatiotemporal scales.

I. Introduction

CO2 studies have comprised an important component of plant biology research for decades, as CO2 is the primary carbon source for photosynthesis and a major driver of climate change. Only 20 000 yr ago, atmospheric [CO2] were among the lowest concentrations that occurred during the evolution of land plants (180–200 ppm). Since then, [CO2] has more than doubled to 401 ppm due to greenhouse gas emissions, representing concentrations that plants have not encountered for several million years (Tripati et al., 2009). Consequently, [CO2] may be rising faster than the rate at which some plant species can evolve to function optimally (Lau et al., 2007; but see Ward et al., 2000). In addition, current levels of plasticity for functional traits may be inadequate to maintain optimal functioning in novel future environments (Franks et al., 2014; Anderson & Gezon, 2015). Over the past several decades, CO2 studies have met with great success in characterizing the effects of elevated [CO2] on leaf-level gas exchange, carbohydrate dynamics, and plant growth (Ainsworth & Long, 2005; Franks et al., 2013). Large-scale studies (particularly free-air CO2 enrichment studies, FACE) have provided further insight into the effects of elevated [CO2] on plant community dynamics and productivity (Norby et al., 2016). Nonetheless, many questions remain about plant responses to rising [CO2], as well as interactions with other changing environmental factors, particularly at the most fundamental mechanistic levels. Specifically, molecular and whole-plant responses to [CO2] scale to influence higher order processes; however, such scaling factors are far from resolved and are highly variable across ecosystems. Additionally, increases in [CO2] are strongly coupled with rising temperatures and drought, and the interactive effects of these drivers on plant functioning are unclear at almost every level. The new generation of FACE studies can help address these challenges by facilitating cross-site analysis of plant-to-ecosystem responses to experimental [CO2] manipulations (Norby et al., 2016). Studies spanning preindustrial through future [CO2] can further provide a baseline for plant functioning before human intervention (Medeiros & Ward, 2013; Becklin et al., 2016). Finally, multigenerational and molecular-level studies can elucidate potential evolutionary responses to [CO2] (Ward et al., 2000; Watson-Lazowski et al., 2016). Later we discuss three topics in CO2 research with immediate consequences for global carbon cycling, food security and ecosystem services (Fig. 1). How does [CO2] affect plant developmental transitions? What are the implications of rising [CO2] for plant–water dynamics? And how does [CO2] impact feedbacks in plant–microbe symbioses? Incorporating the interactive effects of [CO2] and climate as well as questions of scale will be important for understanding each of these topics. Although this is by no means an exhaustive list, we use these examples to emphasize why CO2 research is more critical than ever, and will remain so long into the future.
Figure 1.

Figure 1.

Direct and indirect effects of rising [CO2] on plant development and phenology, plant physiology and water dynamics, and plant interactions with other organisms can have cascading effects on ecological and evolutionary processes across spatial and temporal scales (a). Here we highlight examples of key questions in CO2 research that will require an integrative approach that bridges gaps between molecular biology, plant physiology, ecological and evolutionary biology, and ecosystem science (b). This is by no means an exhaustive list, and not all questions are discussed specifically in the main text. Images show (a1) a developing Arabidopsis flower bud, (a2) stomata (upper image, Juniperus) and xylem (lower image, Picea) structures, and (a3) arbuscular mycorrhizal fungi colonizing herbaceous roots. Images were provided courtesy of R. Atkinson, K. M. Becklin, V. Bui and S. M. Walker. FLT, flowering time; PSF, plant–soil feedback.

II. CO2 effects on plant development and phenology

Numerous studies show that elevated [CO2] can impact plant developmental processes, particularly flowering time (FLT). However, we are just beginning to characterize the mechanisms driving these developmental shifts and their implications for individual plants, communities, and ecosystems. Shifts in FLT can alter the course of evolution, influence community competition, disrupt plant–pollinator interactions and affect crop/food production (Bartomeus et al., 2011; Rafferty & Ives, 2012). In a literature survey, 57% of wild species and 62% of crop species exhibited altered FLT when grown at elevated [CO2], with extreme FLT responses ranging from accelerations of 60 d to delays of 16 d depending on the species (Springer & Ward, 2007). The effects of elevated [CO2] on FLT can also vary within species, such as in Arabidopsis thaliana ecotypes and soybean lines, which exhibited both delayed and accelerated FLT at elevated [CO2] (Ward & Kelly, 2004; Bunce & Hilacondo, 2016). Additionally, plants do not always flower at the same size in novel environments, including elevated [CO2] (Springer et al., 2008; Springate & Kover, 2014). This may be due to CO2 effects on signaling mechanisms that act independently of plant size or growth rate. Thus, rising [CO2] can alter plant size at key life cycle milestones, including flowering (Fig. 2), with possible downstream effects on fitness and carbon cycling.
Figure 2.
(a) A genotype of Arabidopsis thaliana (SG; see Springer et al., 2008) that is sensitive to elevated [CO2] with respect to flowering time. Both representative plants are of the same genotype and age and were grown at 380 and 700 ppm [CO2]. Note that the elevated [CO2] plant has not yet flowered, although it has accumulated more total biomass and a greater number of leaves. (b) Time to visible flowering, (c) total biomass at flowering, (d) total number of leaves at flowering for the SG Arabidopsis genotype (white circles) and CG (green circles, control genotype) grown at 380 and 700 ppm [CO2]. Real-time RT-PCR expression patterns for FLC in (e) SG and (f) CG Arabidopsis genotypes grown at 380 ppm (solid blue line) and 700 ppm CO2 (dashed red line). Sampling was performed at the same developmental stages for each genotype. Signals were normalized to the expression level at the time of flowering at 380 ppm within the same genotype. The photo in (a) is courtesy of B. Burgert, and (b–f) were reproduced from Springer et al. (2008).
Although molecular work in this area is still developing, elevated [CO2] has been shown to affect the expression of flowering genes and regulatory pathways. Specifically, the floral repressor, FLOWERING LOCUS C (FLC), was shown to play a key role in influencing FLT at elevated [CO2] in Arabidopsis. In this case, sustained expression of FLC caused a previously selected genotype to flower much later, with much higher total biomass, and many more leaves at elevated vs current [CO2] (Fig. 2; Springer et al., 2008). Changes in [CO2] also have been shown to regulate the expression of micro RNAs involved in plant development. The miR156 flowering pathway controls the vegetative juvenile-to-adult phase transition and is involved in floral initiation in Arabidopsis (Wang et al., 2009; Wu et al., 2009). A doubling in [CO2] reduced the expression of miR156/157, leading to a 7 d acceleration in FLT (May et al., 2013). Despite these advancements, it is still unclear which upstream processes influence flowering gene expression and micro RNAs during growth at elevated [CO2]. One hypothesis linking elevated [CO2] to altered developmental timing proposes that sugars act as signaling molecules to influence flowering gene expression. Through this mechanism, plant carbohydrate status is sensed in leaves via the metabolite trehalose-6-phosphate (T6P; Wahl et al., 2013; Figueroa & Lunn, 2016), and FLOWERING LOCUS T (FT) is activated when carbohydrate levels become adequate to support reproduction. FT is then translocated to the meristem where floral induction occurs. Elevated [CO2] generally increases the sugar status of leaves, and altered sugar sensing via T6P may be one possible mechanism for how elevated [CO2] influences FLT (Springer & Ward, 2007; Coneva et al., 2012). Studies in which elevated [CO2] or additions of exogenous sucrose were associated with delays in FLT support this potential mechanism (Posner, 1971). Despite the importance of understanding the mechanisms driving CO2 effects on plant development and phenology, research that relates sugar-sensing mechanisms to elevated [CO2] is lacking. Further studies exploring molecular drivers of FLT in model and nonmodel systems will aid in accurately predicting how phenological responses to global change will manifest across spatiotemporal scales.

III. CO2 effects on plant–water dynamics

Although we can predict general patterns of how [CO2] alters stomatal conductance, photosynthesis and transpiration in many systems (Ainsworth & Long, 2005), the strength of these effects (Haworth et al., 2016) and major patterns in CO2-responsiveness across plant groups are still being debated (Brodribb & McAdam, 2011; Franks & Britton-Harper, 2016). Thus, despite decades of CO2 research, surprises remain in how rising [CO2] affects plant–water dynamics (Franks et al., 2013). Many of these questions may be better explained by improving our understanding of how plant hydraulics will respond to a range of [CO2], especially in conjunction with increased drought and warming. When leaves are exposed to elevated [CO2], photosynthesis is stimulated, but stomatal conductance and transpiration decline, increasing leaf water use efficiency. It is commonly assumed that plants grown at elevated [CO2] will therefore use less water and better withstand drought stress; however, this is often not the case (Vaz et al., 2012; Perry et al., 2013; Duan et al., 2014). Elevated [CO2] can increase transpiration or reduce drought tolerance by increasing canopy leaf area (McCarthy et al., 2006; Warren et al., 2011), stimulating nocturnal stomatal conductance (Zeppel et al., 2012), reducing rooting depth (Duursma et al., 2011) and increasing leaf temperatures, via lower latent heat loss (Warren et al., 2011). Even when elevated [CO2] promotes soil water savings at larger spatial scales, changes in plant community composition can increase total leaf area index and transpirational potential (Fay et al., 2012), which may leave ecosystems equally vulnerable to drought under current and future [CO2]. Without a greater understanding of how common these responses are under elevated [CO2], we cannot make robust predictions of how rising [CO2] will alter drought tolerance, or properly capture CO2 effects on ecosystem water-use efficiency (De Kauwe et al., 2013). Plant hydraulic responses to rising [CO2] have received less attention than leaf-level gas exchange responses despite the importance of water transport traits in determining drought tolerance, carbon assimilation, and growth. Hydraulic conductance often decreases at elevated [CO2] (Tognetti et al., 2005; Domec et al., 2009), but may also increase (Domec et al., 2010) or show no response (Locke et al., 2013), and can vary in an apparently species-specific manner that we cannot fully account for (Domec et al., 2010). Likewise, cavitation resistance can increase at elevated [CO2] in some species (Rico et al., 2013), whereas vessel implosion strength, a correlate of cavitation resistance, decreases with rising [CO2] in others (Medeiros & Ward, 2013). These findings highlight that we currently lack a generalized framework for predicting how [CO2] rise will alter hydraulic traits. This issue becomes even more problematic when trying to predict integrated plant function at elevated [CO2] in response to water stress. For example, plants grown at low [CO2] maintained their hydraulic conductance and photosynthesis during drought, whereas these parameters declined in plants grown at elevated [CO2] (Medeiros & Ward, 2013), indicating that rising [CO2] could reduce plant growth and drought tolerance. The uncertainties in how changes in [CO2] affect plant–water balance are exacerbated when we consider that warming, which will increase concurrently with [CO2], usually enhances water stress. Although leaf-level physiological responses to these drivers suggest that rising [CO2] can offset the negative effects of warming, evidence for this is mixed (Dieleman et al., 2012; Way et al., 2015). Instead, a growing number of studies find that elevated [CO2] does not ameliorate the impact of high temperatures on drought stress, particularly when water is severely limited (Wertin et al., 2012; Zeppel et al., 2012; Duan et al., 2014). Resolving the interactive effects of globally uniform increases in [CO2] and regionally variable increases in temperature and drought will be necessary for scaling global change effects on plant–water dynamics.

IV. CO2 effects on plant–microbe interactions

Changes in plant physiology, development and growth with rising [CO2] can influence global change responses at higher biological levels through cascading effects on interactions between plants and other organisms (Gilman et al., 2010). Likewise, direct effects of plant mutualists and antagonists on plant traits and fitness can mediate plant acclimation and evolutionary responses to global change (Lau & Lennon, 2012). CO2 effects on species interactions and subsequent feedbacks between ecological and evolutionary processes may be especially important for plant–microbe symbioses where the functioning and fitness of the interacting organisms are tightly linked (terHorst & Zee, 2016). However, microbial communities, especially those belowground, remain one of the least understood components of terrestrial ecosystems (Bardgett & van der Putten, 2014), which presents a major challenge when modeling CO2 effects across biological scales (Smithwick et al., 2014). Mycorrhizal associations, belowground plant–fungus symbioses in which host plants trade carbohydrates for soil nutrients, are one of the best-studied types of plant–microbe interactions. CO2 effects on mycorrhizal associations have largely been explored in short-term studies from temperate ecosystems in the northern hemisphere, which limits our understanding of mycorrhizal processes at the global scale (Mohan et al., 2014). Additionally, few studies have examined genetic and phenotypic variation in mycorrhizal traits (Johnson et al., 2012), or the interactive effects of multiple global change drivers (Mohan et al., 2014); thus, substantial questions remain regarding mechanisms driving mycorrhizal responses to rising [CO2] (Fig. 1). Traditionally, mycorrhizal associations are viewed as nutritional mutualisms that are most beneficial to host plants when soil nutrients limit plant growth (Johnson & Graham, 2013). For this reason, rising [CO2] is predicted to promote stronger mycorrhizal mutualisms. However, observations of mycorrhizal responses to rising [CO2] do not always correspond to this prediction. In fact, competition between host plants and mycorrhizal fungi for increasingly limited nutrients can result in neutral associations, or even reduce plant growth under elevated [CO2] (Kivlin et al., 2013; Becklin et al., 2016). Recent work calls for a broader view of mycorrhizal associations that incorporates the functional diversity exhibited by mycorrhizal fungi. For example, some fungi stimulate integrated signaling pathways that enhance their host’s ability to tolerate biotic (e.g. herbivore resistance; Pineda et al., 2013) and abiotic stress (e.g. drought tolerance; Worchel et al., 2013). In fact, most phytohormones examined thus far play a role in regulating mycorrhizal associations (Pozo et al., 2015), and common mycorrhizal networks can serve as a conduit for these signals to pass between neighboring plants (Johnson & Gilbert, 2015). How these signals will integrate environmental cues and regulate multidimensional mycorrhizal responses to rising [CO2] in complex natural communities remains unclear. There is growing evidence that within-population variation in mycorrhizal traits can affect mycorrhizal associations and ecosystem processes to the same degree as variation among mycorrhizal species (Johnson et al., 2012). Furthermore, multiple experiments highlight the potential for genetically based variation in mycorrhizal traits to facilitate evolutionary responses to environmental conditions (Johnson et al., 2012; van der Heijden et al., 2015). Thus, it is likely that both inter- and intraspecific variation in mycorrhizal associations will generate feedbacks that can drive plant and community responses to global change (van der Putten et al., 2013; terHorst & Zee, 2016). Characterizing adaptive potential in plant and fungal populations, the strength of selection exerted by rising [CO2] and other global change drivers, and the magnitude of eco-evolutionary feedbacks between mycorrhizal partners will be especially important for scaling mycorrhizal responses to global change.

V. The way forward

Although we have had great success in defining some aspects of plant responses to rising [CO2], large knowledge gaps still remain this field (Fig. 1). Addressing these challenges will require collaboration across disciplines, experiments that span multiple scales of complexity, and the application of new technologies and molecular tools. Examples of this include CRISPR-Cas9 that will allow for genome editing and precise mutations in order to study molecular pathways in ecologically relevant species. Additionally, plants host diverse communities of micro-organisms that can affect molecular- through ecosystem-level processes. Thus, we need to broaden our view of plants to consider how rising [CO2] impacts the physiology, ecology and evolution of these symbiotic communities. Finally, understanding how rising [CO2] over recent geological history has affected plant traits will provide insights into the evolutionary pressures that have shaped modern plant species (Gerhart & Ward, 2010). Using a broader experimental [CO2] gradient will generate more informative response curves (rather than two-point comparisons) of plant and community traits, allowing us to better identify thresholds or nonlinear responses that could surprise us in the future. As we move into an even higher CO2 world, it will be imperative that plant breeding programs account for potential developmental, physiological and ecological shifts that may occur in response to rising [CO2] when developing future crop varieties and biofuels. Moreover, mechanistic studies of plant responses to rising [CO2] will become even more important for predicting global carbon, water and nutrient cycling, and for determining how ecosystem services may shift in the future.


K.M.B., S.M.W. and J.K.W. are supported on NSF IOS #1457236 and a Research Investment Council grant from the University of Kansas. K.M.B. was also supported by a NIH IRACDA Postdoctoral Fellowship, and S.M.W. was supported by NSF IGERT and GK-12 Fellowships. D.A.W. is supported by an NSERC Discovery grant, CFI and an Ontario ERA award.
This article appeared on the New Phytologist website at http://onlinelibrary.wiley.com/doi/10.1111/nph.14336/abstract]]>

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