https://doi.org/10.1093/plcell/koac303 THE PLANT CELL 2023: 35: 24–66 Climate change challenges, plant science solutions Nancy A. Eckardt,1,* Elizabeth A. Ainsworth,2 Rajeev N. Bahuguna,3 Martin R. Broadley,4,5 Wolfgang Busch,6 Nicholas C. Carpita,7 Gabriel Castrillo,4,8 Joanne Chory,6,9 Lee R. DeHaan,10 Carlos M. Duarte,11 Amelia Henry,12 S.V. Krishna Jagadish,13 Jane A. Langdale,14 Andrew D.B. Leakey,15 James C. Liao,16 Kuan-Jen Lu,16 Maureen C. McCann,7 John K. McKay,17 Damaris A. Odeny,18 Eder Jorge de Oliveira,19 J. Damien Platten,12 Ismail Rabbi,20 Ellen Youngsoo Rim,21 Pamela C. Ronald,21,22 David E. Salt,4,8 Alexandra M. Shigenaga,21 Ertao Wang,23 Marnin Wolfe24 and Xiaowei Zhang23 1 Senior Features Editor, The Plant Cell, American Society of Plant Biologists, USA 2 USDA ARS Global Change and Photosynthesis Research Unit, Urbana, Illinois 61801, USA 3 Centre for Advanced Studies on Climate Change, Dr Rajendra Prasad Central Agricultural University, Samastipur 848125, Bihar, India 4 School of Biosciences, University of Nottingham, Nottingham, NG7 2RD, UK 5 Rothamsted Research, West Common, Harpenden, Hertfordshire, AL5 2JQ, UK 6 Plant Molecular and Cellular Biology Laboratory, Salk Institute for Biological Studies, La Jolla, California 92037, USA 7 Biosciences Center, National Renewable Energy Laboratory, Golden, Colorado 80401, USA 8 Future Food Beacon of Excellence, University of Nottingham, Nottingham, NG7 2RD, UK 9 Howard Hughes Medical Institute, Salk Institute for Biological Studies, La Jolla, California 92037, USA 10 The Land Institute, Salina, Kansas, USA 11 Red Sea Research Center (RSRC) and Computational Bioscience Research Center, King Abdullah University of Science and Technology (KAUST), Thuwal, 23955-6900, Saudi Arabia 12 International Rice Research Institute, Rice Breeding Innovations Platform, Los Ban~os, Laguna 4031, Philippines 13 Department of Plant and Soil Science, Texas Tech University, Lubbock, Texas 79410, USA 14 Department of Biology, University of Oxford, Oxford, OX1 3RB, UK 15 Department of Plant Biology, Department of Crop Sciences, and Institute for Genomic Biology, University of Illinois at Urbana-Champaign, Illinois 61801, USA 16 Institute of Biological Chemistry, Academia Sinica, Taipei 11528, Taiwan 17 Department of Agricultural Biology, Colorado State University, Fort Collins, Colorado 80523, USA 18 The International Crops Research Institute for the Semi-Arid Tropics–Eastern and Southern Africa, Gigiri 39063-00623, Nairobi, Kenya 19 Embrapa Mandioca e Fruticultura, Rua da Embrapa, Cruz das Almas, BA, Brazil 20 International Institute of Tropical Agriculture (IITA), PMB 5320 Ibadan, Oyo, Nigeria 21 Department of Plant Pathology and the Genome Center, University of California, Davis, California 95616, USA 22 Innovative Genomics Institute, Berkeley, California 94704, USA 23 National Key Laboratory of Plant Molecular Genetics, Center for Excellence in Molecular Plant Sciences, Institute of Plant Physiology and Ecology, Chinese Academy of Sciences, Shanghai 200032, China 24 Auburn University, Dept. of Crop Soil and Environmental Sciences, College of Agriculture, Auburn, Alabama 36849, USA *Author for correspondence: neckardt@aspb.org Authors are listed alphabetically (with the exception of the lead author/coordinating editor). All authors contributed to writing and revising the article. The author responsible for distribution of materials integral to the findings presented in this article in accordance with the policy described in the Instructions for Authors (https://academic.oup.com/plcell) is: Nancy A. Eckardt (neckardt@aspb.org). Received June 21, 2022. Accepted September 29, 2022. Advance access publication October 12, 2022 VC The Author(s) 2022. Published by Oxford University Press on behalf of American Society of Plant Biologists. Open Access This is an Open Access article distributed under the terms of the Creative Commons Attribution License (https://creativecommons.org/licenses/by/4.0/), which permits unrestricted reuse, distribution, and reproduction in any medium, provided the original work is properly cited. PerspectiveDownloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 25 Abstract Climate change is a defining challenge of the 21st century, and this decade is a critical time for action to mitigate the worst effects on human populations and ecosystems. Plant science can play an important role in developing crops with en- hanced resilience to harsh conditions (e.g. heat, drought, salt stress, flooding, disease outbreaks) and engineering efficient carbon-capturing and carbon-sequestering plants. Here, we present examples of research being conducted in these areas and discuss challenges and open questions as a call to action for the plant science community. Introduction possibilities, stimulate further research, and motivate plant scientists at any stage of their careers to become involved in Climate change is caused by an accumulation of greenhouse work aimed at mitigating climate change and enhancing gases (GHGs) (e.g. CO2, methane) in the atmosphere leading food and energy security. Mitigating the climate change cri- to increased planetary heat-trapping and global warming. sis will require all hands on deck. The IPCC Sixth assessment report (IPCC, 2022) strongly sug- gests that limiting global warming to 1.5C above pre- How can more carbon be retained in soil and industrial levels will be needed to avoid severe climate biomass? change effects. This will require halving global CO2 emissions by 2030 and cutting them to net zero by 2050, as well as re- Carbon sequestration in annual cropping systems moving an additional 2–10 billion metric tons (Gt) of CO2 (By John K. McKay) each year. In some locations, warming may benefit certain Annual cropping systems present opportunities for carbon crops, and, over time, the optimal growing regions may shift sequestration that have yet to be exploited. In addition to farther away from the equator. However, the effects of cli- the need to reduce GHG emissions, active atmospheric CO2 mate change are not limited to increasing temperatures and removal strategies, also called Negative Emissions heatwaves in many parts of the world but include changes Technologies (NETs), are needed to attain net CO2 reduc- in rainfall, more severe and frequent storms, increased tions and avoid the most damaging climate change out- drought, and increased threat of wildfires. All of these effects comes (National Academies of Sciences, Engineering, and are anticipated to adversely affect crop yields and food secu- Medicine, 2019). Atmospheric CO2 removal technologies rity worldwide within the next 20 years (Zhao et al., 2017; Li need to be implemented now and increase to levels on the et al. 2019; Jägermeyr et al., 2021). As the impact of climate order of 10 Gt CO2 per year by 2050, and 20 Gt CO2 per change on crop systems intensifies, the need to develop year by 2100 (National Academies of Sciences, Engineering, stress-resilient crops to combat food insecurity rises. and Medicine, 2019). In this article, we explore several ways in which plant sci- Among NET for CO2 removal, soil carbon sequestration is entists are working on solutions related to carbon sequestra- the least expensive and most ready to scale in the next dec- tion to help achieve net zero CO2 emissions and crop ades (National Academies of Sciences, Engineering, and improvements to protect and enhance yields for increased Medicine, 2019). Current US cropping systems use genetics food security. The first section outlines challenges and that were not designed to minimize GHG emissions nor to approaches for enhancing the carbon sequestration capacity maximize carbon sequestration, yet heritable genetic varia- of crops (annual and perennial) and seagrasses, followed by tion for these traits exists in many crops. In addition, agricul- a section on improving photosynthesis. A third section tural soils experienced well-documented decreases in soil addresses engineering climate resilience in crops (resistance carbon over the last century (Davidson and Ackerman, or tolerance to abiotic and biotic stresses). The final section 1993) and are capable of sequestering all of the CO2 cur- describes the vision of a sustainable global bioeconomy rently in the atmosphere (Ciais et al., 2013). Here, I review rooted in plant biology. We acknowledge that there are the challenges with attempts to achieve soil carbon seques- other areas, not covered here, in which plant science can tration in current annual cropping systems, both with the play a role in mitigating adverse climate change effects, in- way in which the maize (Zea mays)–soy (Glycine max) rota- cluding bioenergy, forestry, and ecosystem conservation. tion was designed and the science to date on how manage- Solutions in all of these areas are needed in the very near fu- ment might lead to predictable increases in soil carbon. I ture, and in the longer term. We do not provide an in- then focus on genetic changes that are needed to create depth review of these topics. Rather, the examples provided carbon-negative crops, including optimal combinations of here illustrate a few of the many avenues of research being traits that can be addressed in breeding programs. conducted by plant scientists around the world. A compan- The major, unaddressed problem for sustainability and ion review by Verslues et al. (2023) addresses unresolved GHG emissions in annual cropping systems is excess nitro- questions in plant abiotic stress. We hope that these stories gen (N) in the form of synthetic fertilizer (Northrup et al., help to inform the plant science community of the 2021), which leaches into groundwater, rivers, and oceans Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 26 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. and into the atmosphere as N2O, a GHG with an effect size (Oryza sativa), breeding during the Green Revolution led 300 that of CO2 (Albritton et al., 2001). An obvious ex- to the fixation of mutations that reduce NUE (OsTCP19; ample is ethanol production from maize, where N is respon- Liu et al., 2021b) and root growth (Dro1; Arai-Sanoh sible for 480% of GHG emissions overall (Kim et al., 2014). et al., 2014) in the elite breeding lines. For the parts of the world where the Green Revolution was It is worth considering the traits of an ideal annual crop successfully deployed (Evenson and Gollin, 2003), a major for carbon-negative supply chains for food, feed, fiber, and consequence is the exclusive use of crop genotypes that re- fuel. As mentioned, genetic changes to lower N require- quire high N inputs. To fix this N problem, we need to im- ments and create deeper, more massive root systems can prove N use efficiency (NUE) and greatly reduce N input. make annual biomass feedstock production carbon negative Increasing NUE is feasible (Hirel et al., 2007; Northrup et al., (Paustian et al., 2016a). Another key trait for carbon seques- 2021) and can be achieved in part by removing a small tration is population density, where increasing the number number of large-effect mutations that were selected to high of individuals per hectare leads to more root systems and frequency in elite germplasm in the Green Revolution greater carbon input. Crop species that were not part of the (Moyers et al., 2018). Getting farmers to reduce N input is a Green Revolution have promise in this respect (Amaducci much greater challenge. First, overfertilizing every other year et al., 2008). For example, industrial hemp (Cannabis sativa) is a well-established management practice of the maize-soy was never bred for high N inputs, can be grown at popula- rotation that encompasses 73 million hectares of farmland tion densities of 500,000 plants per hectare, and has greater in the USA. Although soybean is an N-fixing species, in root biomass below 50 cm than other major crops modern cropping systems high-yielding soy crops require (Amaducci et al., 2008). Root carbon composition is also a hundreds of kilograms of N per hectare (Salvagiotti et al., genetic target, as some forms of carbon may be more recal- 2008). Although fertilizer has recently increased in price, so citrant to degradation and therefore longer lived in soils. have crop commodity prices, and thus farmers remain in- The idea of engineering roots to create more recalcitrant centivized to maximize N inputs. In the USA, the maize–soy forms of carbon, such as suberin, is discussed below by rotation is highly subsidized by federal funds in the form of Busch and Chory. Suberin is one example; another is lignin, direct payment to farmers as well as mandates on using eth- which is a parameter in models of soil carbon (Parton, anol from fermentation of maize grain and biodiesel from 1996). We found large heritable variation in percent lignin in transesterification of soy lipids. maize roots (Figure 1) and are testing the prediction that Most efforts in using annual cropping systems for soil car- genotypes with greater root lignin will lead to greater quan- bon sequestration have focused on changes in management tity and durability of soil carbon. that were originally designed for soil health (Ogle et al., Root exudates, a diverse set of simple carbon molecules 2019), such as reduced tillage, greater residue retention, and that are released passively or actively into the soil, also con- cover crops that are designed to increase the amount of tribute to soil organic carbon (SOC). Little is known regard- above-ground plant biomass left in the field per unit area ing the degree to which root exudates are controlled by per year (McClelland et al., 2021). Most of the published studies on the effect of management on soil carbon are lim- genetics versus the environment. Even less is known about ited to the top 30 cm of soil, which is where most of the the genetic control of the abundance and composition of carbon inputs are expected (Ogle et al., 2019). However, this root exudates, even in model species. This is due in part to top 30 cm is also the least durable soil carbon and can re- the difficulty of measuring the relevant phenotypes in agri- spire back into CO2 in a few years. Getting soil carbon culturally relevant environments. On the soil modeling side, inputs deeper into the soil is needed to achieve greater and recent progress has been made in separating biomass and more durable carbon sequestration in agricultural systems exudate inputs to soil carbon, where exudates are predicted (Paustian et al., 2016a, 2016b, 2019) and will require genetic to lead to increases in mineral-associated organic matter, changes in crops. which in turn is predicted to have a longer residence time Genetic changes in annual cropping systems are needed than other soil carbon fractions (Zhang et al., 2021b). both to reduce inputs (Northrup et al., 2021) and achieve Finally, the soil and root microbiome, which is influenced by carbon sequestration levels of tons per hectare per year root exudates and plant genotype (Peiffer et al., 2013; (Paustian et al., 2016a). Some changes can be achieved by Wagner et al., 2020; Favela et al., 2021), influences the car- selecting against large-effect mutations that went to high bon retention properties of soils, although data on effect frequency during the Green Revolution. Prior to the sizes are lacking (Naylor et al., 2020). Ectomycorrhizae are Green Revolution, putting large amounts of synthetic N thought to be key drivers of SOC accumulation in forests on agricultural fields reduced yield, as tall crops heavy (Soudzilovskaia et al., 2019) and could be exploited in crop- with grain were highly prone to lodging. In many cases se- ping systems. Manipulating the soil and root microbiome of lection during the Green Revolution was based on recur- cropping systems at scale will be much more difficult than rent backcrossing to dwarf lines and involved small obtaining seed from new crop genotypes but is a possible effective population sizes and low levels of effective re- tool for engineering annual cropping systems for enhanced combination (Moyers et al., 2018). For example, in rice carbon sequestration. Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 27 the amount of the natural product suberin in roots. Suberin is a lipophilic complex polyester that is composed of very long-chain fatty acids and polyaromatic compounds. Suberin may be a good source for stable SOC due to its intrinsic bio- chemical stability (Lorenz et al., 2007) and its interaction with soil minerals and occlusion in topsoil microaggregates (Kell, 2012; Lin and Simpson, 2016). We note that there are numerous other plant traits that promise to be useful for enhancing the capacity of plants to sequester carbon in the soil (see some additional examples in the previous section by McKay). There are several significant challenges to utilizing crops for carbon sequestration. Genetic trait enhancement is a lengthy process and its adoption by the public will be chal- lenging. Establishing a link between root traits and carbon Figure 1 Quantitative variation in lignin content in maize root sys- tems from a field study of 358 maize inbred lines. A description of the accumulation and permanence in agricultural soils will re- experiment can be found in Woods et al. (2022). quire substantial experimental efforts. Carbon accumulation and persistence are also dependent on soil type, climate Harnessing plants: A global initiative to enhance parameters, and agricultural practices such as the use of plant-based carbon sequestration cover crops and no-till farming (Schmidt et al., 2018). (By Wolfgang Busch and Joanne Chory) Although there is good potential for plant-based carbon se- questration in the surface soil layer (up to 1.85 Gt C/year in We consider solutions for carbon sequestration based on the top 30 cm of global cropland soils alone; Zomer et al., plants’ abilities to draw down CO2 from the atmosphere via photosynthesis and convert it to biomass. Earth’s soils con- 2017), an enhanced rooting depth and altered biochemical tain a large amount of carbon, estimated at approximately makeup of roots could yield a much larger sequestration ca- 2,300 Gt carbon to 3-m depth, which constitutes about pacity. Finally, time is pressing—every year that goes by three times the current atmospheric pool of CO without significant carbon drawdown will negatively impact 2 (Schlesinger and Bernhardt, 2020). The main source of SOC billions of humans and decrease the biodiversity of our is plant material (e.g. aboveground plant biomass, roots, and planet. root exudates), which can be stored in the soil or respired The Salk Harnessing Plants Initiative is working to identify back into the atmosphere. It is estimated that cropland and genetic and molecular mechanisms to increase root biomass, grazing land soils (about 5 billion hectares globally) have an root depth, and suberin root content. We use examples of enormous capacity for storing carbon (Sanderman et al., this research to highlight considerations for plant-based car- 2017). Combined with existing agricultural infrastructure, bon sequestration that we have identified during this work. this capacity provides an opportunity to leverage genetics to Each of the target traits comes with specific challenges and improve traits related to plant-mediated carbon opportunities. For instance, increased root mass will elevate sequestration. the carbon input into soils and can improve the ability of Several plant traits are good candidates for facilitating roots to forage for nutrients and water. However, increasing plant carbon sequestration (Figure 2). Root biomass is one, root mass beyond a certain level might come at the expense as it is estimated that a given mass of root inputs contrib- of yield. Nevertheless, the relationship between root biomass utes about five times more SOC than the equivalent mass and yield is not necessarily a zero-sum game as enhanced of aboveground litter (Jackson et al., 2017). However, traits water and nutrient uptake of a bigger root system can sup- associated with mechanisms that increase recalcitrance of port a larger shoot. This might be particularly relevant under SOC to breakdown by soil microorganisms (SOC protection) drought or nutrient-limited conditions. An example of the will also be required to increase residence time in soils. lack of a strict tradeoff of root biomass and yield in major Mechanisms of SOC protection include a complex interplay crops is the lack of correlation of yield and root biomass in between the chemical makeup of SOC, physical occlusion of maize as well as soybean in a multi-location, multi-year SOC within soil aggregates, formation of stable organo- study (Ordón~ez et al., 2020). Increasing root depth promises mineral complexes, and water-film connectivity between to increase the lifetime of the average carbon molecule de- SOC and microbes (Schmidt et al., 2011; Lehmann et al., posited by roots in the soil, provide roots access to deeper 2020). More than half of the global SOC is found in deep soil layers that can contain more moisture, and facilitate the soil layers (Jobbágy and Jackson, 2000), and the mean resi- capture of nitrate that leaches deeper into the soil during dence time of SOC increases with depth, implying lower de- the growing season. However, surface roots are still impor- composability of root-derived carbon in deeper soil layers tant for foraging immobile nutrients such as phosphorus. (Gill et al., 1999; Prieto et al., 2016). Root biochemistry also Therefore, achieving an optimal balance between shallow influences decomposability, and a prime candidate trait is roots and deep roots will be important. As an effective Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 28 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. Figure 2 Toward an ideal carbon-capturing crop plant. A, The ideal plant should accumulate suberin in the cell wall of its root cells and form a vast and deep root system. To realize this goal, the existing literature and experimental evidence are curated to look for candidate genes affecting root system architecture and root mass. This information is combined with root-specific promoters and suberin biosynthetic genes. B, The ideal plant is created by capitalizing on both classical (breeding) and more recent (genome editing, genetic engineering) approaches to introduce favor- able alleles and genes that will increase root biomass and transgenes that will increase the deposition of suberin in the root. In addition to trap- ping more carbon, these ideal plants will replenish carbon-depleted soils with degradation-recalcitrant carbon polymers (indicated by the darker color of the soil on the right). Figure credit: P. Salomé. apoplastic barrier, suberin in specific areas of the root could To quantitatively link these root traits to carbon charac- provide enhanced flood and drought resilience and might teristics in the soil, we are working with soil scientists to enhance root growth in deeper, more anoxic layers of the better estimate the soil carbon impact of crop varieties that soil. Extensive variation for each of these traits between and have different root mass, depth, and suberin content. We within species indicates that there are genetic mechanisms aim to test the effects of genetic alterations via gene editing that can be leveraged to improve them. or gene engineering approaches in crops over the next few Our work in enhancing these traits is being conducted in years. Recent advances in high-throughput phenotyping, se- parallel with model plants via forward and reverse genetic quencing, and functional single-cell genomics now provide a approaches, as well as in diversity collections of major row way to leverage genes, gene constructs, and genetic variants crops and cover crops to identify crop-specific targets using within and between species. We aim to have the proof of genome-wide association studies (GWASs). While we are in- concepts for enhanced crop traits within the next 3 years to terested in trait changes that will work in the field and then partner with both NGOs and agriculture companies to maintain crop productivity, it is not feasible to measure all enhance varieties that are of interest to farmers. these root traits in the field at high throughput. We there- There are numerous other opportunities for plant biolo- fore rely on initial screening approaches in the laboratory or gists to contribute to climate change mitigation efforts, the greenhouse to measure and engineer root traits, subse- ranging from work on traits that will reduce agricultural quently moving to in-soil or field-testing with a subset of N2O or methane emissions to creating carbon lines that display distinctive traits. We focus on root mass in sequestration-friendly microbiota or mycorrhizal associa- relation to depth, as the engineering or breeding goal is to tions. As a community, we should think of and work toward direct as much root mass as possible to a deeper depth, and promising plant biology-based solutions. on enhancing the accumulation of suberin. Suberin is a highly effective apoplastic diffusion barrier and producing it Rapid de novo domestication of perennial crops everywhere in the root would be detrimental to plant (By Lee R. DeHaan) health. Therefore, we focus on specific root tissues that al- Most agricultural soils have lost 50%–70% of the SOC that ready produce suberin such as the periderm or the exoder- they had previously accumulated under native plant com- mis, which are outer layers in mature root systems. We are munities; therefore, raising the carbon levels in historically targeting such tissues as suberin sinks by using tissue- tilled agricultural soils offers the potential to partially miti- specific promoters to drive suberin production, as well as gate climate change by capturing 30–60 Gt of organic car- utilizing genes involved in the formation of these tissues to bon (Lal, 2003). The restoration of SOC in agricultural soils produce additional tissue layers. would not only mitigate climate change through Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 29 sequestration but would also contribute to adaptation to quality (Audu et al., 2022) is being developed through wide climate change by developing soils with greater nutrient hybridization (Hayes et al., 2018). A direct domestication holding capacity, resistance to erosion from extreme rain program is underway to develop the perennial sunflower rel- events, increased water infiltration, and water storage to sta- ative Silphium integrifolium into a dual-purpose forage and bilize productivity in the face of erratic rainfall (Blanco- grain crop (Van Tassel et al., 2017). Various perennial legu- Canqui et al., 2013). minous species are also being considered for their suitability Although planting long-lived perennial plants on degraded for use as perennial grains (Schlautman et al., 2018). agricultural soils would be one of the most effective ways to Perennial flax (Linum) species are being evaluated for direct rapidly restore soil carbon levels, this approach is limited be- domestication as perennial oilseeds (Tork et al., 2019). cause the herbaceous perennials currently available for use Direct domestication of the cool season perennial grass in agriculture (mainly forage crops) produce biomass that is species intermediate wheatgrass (Thinopyrum intermedium; unsuitable for direct human consumption (Paustian et al., Figure 3) was initiated in the 1980s, and now the harvested 2016a). Therefore, efforts are underway to develop new crop grain is being produced and sold in North America under plants that would have extensive long-lived root systems the trade name Kernza (DeHaan and Ismail, 2017). With its and would achieve carbon sequestration levels similar to pe- extensive root system (Sprunger et al., 2019), the crop has rennial biofuels (Crews and Rumsey, 2017; Dheri et al., 2022) potential for carbon storage belowground (De Oliveira et al., while simultaneously producing abundant human-edible 2020) and to accumulate microbial necromass (Peixoto protein, starch, and oils through mechanically harvestable et al., 2020). However, genetic improvement for grain yield is grain (Glover et al., 2010). needed, since selected populations still have a yield potential Efforts to develop perennial grain crops began decades of less than half that of bread wheat (Triticum aestivum) in ago, but recent advances in genetics and breeding are accel- the same region (Culman et al., 2013). In addition to the erating the timeline and the first successful perennial grains currently limited genetic potential for grain yield, the crop are now entering fields and markets. A perennial rice breed- faces many challenges. New crops always struggle with the ing program was initiated in 1996, targeting the roughly 19 need to coordinate supply chain development in concert million hectares of upland rice grown worldwide where for- with expanding acreage. Novel perennial grains also intro- est land is often cleared and degraded (Sacks et al., 2003). duce a new array of challenges for farmers and agronomists, Annual rice (Oryza sativa ssp. indica) and the rhizomatous such as controlling pests and diseases and managing for sus- perennial relative Oryza longistaminata were hybridized, and tained yield over many years. With intermediate wheatgrass, a breeding program has produced lines for flooded paddies the decline in yield that occurs in aging stands is an ongoing that persist through eight harvests with yields and quality challenge (Pinto et al., 2021). traits on par with modern rice cultivars (Huang et al., 2018; Recent developments in plant biology, genetics, and Hu et al., 2022). Perennial paddy rice is expected to reduce breeding have opened the door to breeding new crops with GHG emissions and water consumption relative to annual carbon-storing perennial root systems and abundant grain rice (Oda et al., 2019). The development of perennial rice for production at a time scale that can proceed at the pace of upland conditions also remains possible in the near term. commercial enterprise development (Runck et al., 2014). Perennial grain sorghum is being developed through wide Low-cost genome sequencing and innovative genome as- hybridization of annual grain sorghum (Sorghum bicolor) sembly approaches are allowing the rapid generation of ref- with perennial species (Figure 3). Progress for yield and sur- erence sequences even for large-genome perennial species. vival has been made by selecting among progeny of crosses Genomic information is now leveraged to perform genomic between S. bicolor and the tetraploid perennial Sorghum selection (Meuwissen et al., 2001) which can greatly acceler- halepense, and evaluation under tropical conditions suggests ate the breeding of perennial crops. Whereas traditional no barrier to high-yielding perennial varieties in warmer breeding of a perennial crop might require 5 or more years regions (Cox et al., 2018b). Recently, diploid perennial grain per generation, involving field evaluation of multiple years sorghum lines have been derived from diploid  tetraploid followed by intermating of selected individuals, genomic se- crosses (Cox et al., 2018a) and from crosses between S. bi- lection uses a genomic prediction model based on the per- color and the perennial diploid species Sorghum propinquum formance of plants grown from multiple generations over (Foster et al., 2020). Working at the diploid level is expected many years. Applying genomic models to genetic marker to expedite the development of perennial grain sorghum by data from seedlings of intermediate wheatgrass has accu- simplifying crosses between perennial germplasm and locally rately predicted mature plant performance (Crain et al., adapted S. bicolor varieties. Now, marker-assisted selection is 2021). Speed breeding (Watson et al., 2018) paired with ge- being initiated to accelerate progress in breeding for traits nomic selection has the potential to further accelerate pe- related to perenniality and productivity (Cox et al., 2018b). rennial crop improvement by increasing the number of A wide array of perennial grain crops could likely be devel- generations that can be completed per year. Genomic selec- oped either by direct domestication of wild perennial spe- tion with speed breeding is currently being implemented cies or wide hybridization between crops and related with intermediate wheatgrass to complete two full cycles of perennials. Perennial wheat with potential to improve soil selection per year, compared to one cycle every 3 years with Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 30 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. Figure 3 Examples of wide hybridization and direct domestication to develop perennial grains. The wild perennial Sorghum halepense (A) was hy- bridized with the domestic species Sorghum bicolor (B) and selective breeding of the progeny produced lines with intermediate head and seed size (C) and the ability to regrow from underground rhizomes (D). In an example of direct domestication, the mostly wild grass Thinopyrum inter- medium can be harvested with conventional equipment (E) and cleaned to obtain a human-edible grain (F) that has properties similar to wheat, as seen in this loaf made with an 80/20 blend of wheat and Th. intermedium flour (G). Domesticated Th. intermedium types now possess domesti- cation traits, such as shatter resistance (H, at right). classical approaches. Although these methods hold great of “orphan” perennial grain species is another approach wor- promise, they remain to be validated across the many re- thy of investigation. Pigeonpea (Cajanus cajan) is an N-fixing peated cycles of selection necessary to produce a highly pro- semi-perennial shrub that is grown in Asia and southern ductive domestic crop. Africa. Although types that can be grown for several seasons The application of genome editing techniques to the do- without replanting have been used in erosion control and mestication of wild species creates exciting possibilities to are still grown by some farmers, annual pigeonpea is now compress the development timeline for new crops (Zsögön the dominant form. A recent study in Malawi indicated that et al., 2018). For instance, by comparing the genome se- farmers are less likely to adopt erratically performing peren- quence of the perennial Thinopyrum intermedium with re- nial pigeonpea due to social pressures and lack of trust in lated domestic grains, targets for genome editing to obtain the technology (Grabowski et al., 2019). Expanded acreage domestic phenotypes have been identified and a roadmap of soil-conserving perennial pigeonpea may depend on the for rapid domestication established (DeHaan et al., 2020). development of improved management techniques spread Although new crop development is the primary approach through peer learning, and new cultivars that enable consis- being used to produce new perennial grains, the rediscovery tent production. Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 31 The basic genetic and physiological control of the peren- research may provide additional insights on their role. nial growth habit has only recently been the subject of ex- Further efforts in resolving carbon concentration mecha- perimentation and remains poorly understood (Park et al., nisms and the role of the microbiome, specifically the root 2017). This lack of understanding has thus far hindered the component, offer promise to contribute to developments in development of perennial grain crops. With a clear under- carbon capture technologies and to increase the efficiency standing of the pathways involved, rapid conversion of exist- of seagrass restoration, respectively. ing annual crops into perennials could be possible. Combined approaches of wide hybridization, genome edit- What do we know? ing, mutagenesis, and transgenics could be used to achieve The high productivity of seagrass meadows even under low perennial growth in high-yielding cultivars. Because the need light conditions (Duarte and Chiscano, 1999) supplies much for carbon sequestration in soils is urgent, these approaches of the carbon sequestered in seagrass meadows (Kennedy could be implemented in parallel, following the approach et al., 2010). The keys to the high productivity of seagrass used to develop COVID vaccines (Ball, 2020) to develop an meadows are efficient light use (Enrıquez et al., 1994), low array of high-yielding perennial crops in the coming years. nutrient requirements (Duarte, 1990), and carbon concen- trating mechanisms that allow seagrasses to use both CO2 The promise of seagrasses for carbon capture and and HCO3 to support their high photosynthetic rates storage (Larkum et al., 2006). The analysis of the full genome se- (By Carlos M. Duarte) quence of the seagrass Zostera marina pointed to a number Seagrasses are a group of about 74 angiosperm species that of evolutionary adaptations required for these species to col- complete their life cycle in the marine environment, where onize the ocean from freshwater angiosperm ancestors they form lush meadows that rank amongst the world’s (Olsen et al., 2016). Some of these adaptations help explain most productive ecosystems (Duarte and Chiscano, 1999; their high carbon removal, including the loss of volatiles, Hemminga and Duarte, 2000). Seagrass meadows are consistent with the loss of stomata through which they are strongly autotrophic, producing more organic matter than emitted for airborne communication and plant defense, consumed in the ecosystem (Duarte et al., 2010) and acting, which reduces losses of carbon and the probability of infec- therefore, as sinks for CO2, much of which is buried in sea- tions, as stomata are a main entry point for pests and grass soils (Duarte et al., 2005, 2013a; Fourqurean et al., pathogens in terrestrial plants (Olsen et al., 2016). 2012). The role of seagrasses as intense carbon sinks in the The seagrass genome also revealed new combinations of biosphere is supported by their high photosynthetic effi- structural traits related to the cell wall, enabling the synthe- ciency, low nutrient requirements, adaptations that mini- sis of cutin-cuticular waxes, suberin–lignin near the plasma mize carbon losses, and their capacity to cope with anoxic, membrane, and macroalgal-like sulfated polysaccharides sulfide-rich sediments. Indeed, whereas seagrasses occupy an (Olsen et al., 2016), recently confirmed by direct analyses of estimated 0.08% of the ocean seafloor, they contribute an the seagrass cell walls, which revealed the presence of estimated 12.7% of all organic carbon annually buried in the fucose-containing sulfated polysaccharides, apiogalacturonan ocean seafloor (Duarte et al., 2005). Yet at least one-third of and lignin (particularly in roots and rhizomes; Pfeifer et al., the historical global area occupied by seagrasses has been 2022). This composition, together with low N and phospho- lost, leading to the loss of this carbon sink and the risk of rus content, renders seagrass tissues highly recalcitrant to remineralization and subsequent CO2 emission of the car- microbial degradation (Enrıquez et al., 1993), helping to ex- bon stocks accumulated in their soils over millennia. Hence, plain high seagrass-derived lignin concentrations in seagrass seagrass meadows represent a key component of the so- soils (Nakakuni et al., 2021) and the high organic carbon called “blue carbon” strategies aimed at avoiding losses and preservation supporting high carbon sequestration rates. restoring coastal vegetated habitats to contribute to climate The full genome sequence conducted to date excluded en- change mitigation, through carbon capture and storage, and dophytic prokaryotes (Olsen et al., 2016), which also have climate change adaptation through the coastal protection important contributions, as exemplified by the recent dis- seagrasses offer (Duarte et al., 2013a; Macreadie et al., 2021). covery of a symbiosis with an N-fixing, root-endophytic bac- A range of tools within plant sciences, from genomics and teria, which helps explain the high productivity of seagrass metabolomics to microbiome investigations are providing in oligotrophic environments (Mohr et al., 2021). important insights into the underpinnings of the remarkable Seagrass morphology is a basic underpinning of their role carbon capture capacity of seagrass. Whereas the role of sea- in carbon removal. They are able to form dense canopies, grasses in carbon capture and storage has been addressed exceeding 15 m2 of leaf surface per m2 of ground covered largely through the quantification of stocks (Fourqurean (Romero et al., 2006), and their rhizomes and roots also et al., 2012) and burial rates (Duarte et al., 2005, 2013a), sea- form a dense web in the sediments, with 0.18–3 m2 of rhi- grass traits related to carbon capture and storage have been zome per squaremeter and 0.47–1 m2 of roots per square- poorly addressed. Here, I discuss the fundamental plant meter of soil (Duarte et al., 1998). The dense web of traits that render seagrasses so efficient in carbon removal seagrass leaves acts as a filter that retains particles entrained and identify a number of promising areas where further in the flow and dissipates wave and turbulent energy, Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 32 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. enhancing the deposition and retention of particles in their Known unknowns soils (Hendriks et al., 2008). Meanwhile, the dense web of Carbon concentrating mechanisms that allow seagrasses to rhizomes and roots in the sediments injects a significant support their high photosynthetic rates and circumvent fraction of seagrass net production (2.8%–48.6% of total net boundary-layer rate-limiting effects are not fully resolved production; Duarte et al., 1998) into the soil and provides (Larkum et al., 2006). Seagrass carbon metabolism remains physical cohesion, thereby reinforcing the soils against the poorly understood and seems to neither fully conform to C4 erosive force of storms and extreme-energy events, such as nor Crassulacean acid metabolism (Larkum et al., 2006). tsunamis (Chatenoux and Peduzzi, 2007; Sasa et al., 2012). Genomic analyses conducted to date have focused on the Rhizome growth and meristematic dominance are the seagrass genome and ignored the rich community of endo- keys to the exponential clonal growth of seagrasses, which is phytes. There is a growing number of analyses of the sea- a major driver of the efficiency of seagrass restoration proj- grass microbiome, including bacteria and fungi (Tarquinio ects in restoring seagrass carbon removal (Duarte et al., et al., 2019; Garcias-Bonet et al., 2021; Torta et al., 2022), but 2013b), as demonstrated in assessments of the carbon re- they remain mostly descriptive and functional analyses are moval benefits of seagrass restoration (Marbà et al., 2015; limited, despite evidence that endophytes may play a major Oreska et al., 2020). Seagrass restoration traditionally was role in supporting nutrient metabolism (Mohr et al., 2021) small in scale and relatively expensive and inefficient, largely and detoxification (Crump et al., 2018). For instance, re- due to small planting units (van Katwijk et al., 2016). cently discovered cable bacteria in seagrass roots could alle- However, observations from hundreds of restoration projects viate critical sulfide toxicity and promote nutrient uptake by (van Katwijk et al., 2016) have led to major recent successes, mobilizing soil iron and phosphorous with acidification asso- such as the cost-effective restoration of 36 km2 of Zostera ciated with electrogenic sulfide oxidation, and by stimulating marina meadows in Virginia’s coastal waters, with major car- dissimilatory nitrate reduction to ammonium and even fix- bon removal benefits (Orth et al., 2020), as well as the long- ing N2 (Scholz et al., 2021). term success of Posidonia australis restoration in SW Opportunities around unknown unknowns Australia, again coupled with important carbon removal benefits (Marbà et al., 2015). Hence, seagrass restoration has Overall, limited progress has been made in applying modern a significant scope to contribute to climate action concepts and tools of plant science to further our understand- (Macreadie et al., 2021). There is ample scope for plant sci- ing of seagrass carbon removal, where an ecological focus pre- ence to contribute to enhancing the success of seagrass res- vails. This is not surprising given that seagrasses represent only toration, through, for instance, the use of probiotic 0.02% of angiosperm species and have little scope to emerge applications (Peixoto et al., 2022) or selective breeding of as model organisms. Yet, the strong selection pressure required seagrasses used for restoration to enhance their resistance, for angiosperms to cope with life in the marine environment and thereby restoration success, in areas experiencing ma- and anoxic, sulfide-rich sediments is likely to have generated rine heat waves (Zabin et al., 2022). novel mechanisms that can open new pathways in biotechnol- Lack of oxygen in seagrass soils, where oxygen penetration ogy. Understanding the carbon concentration mechanism of is limited to the top few mm of seagrass soils, slows down seagrass can open the door for hybrid photosynthesis technol- microbial degradation and the bioturbation activity of ben- ogies for carbon removal (Kornienko et al., 2018), while resolv- ing the functional role of their microbiome can help improve thic fauna, thereby improving the efficiency of carbon burial. the outcomes of seagrass restoration. The limited effort of Anoxic sediments support sulfate-reducing bacteria, produc- plant science on seagrass research to date suggests the exis- ing sulfide that is toxic to seagrass. However, seagrasses pro- tence of “unknown unknowns” and, therefore, a potential for tect themselves from toxic sulfide intrusions by releasing new discoveries that can lead to applications in carbon re- oxygen through their roots, transported from photosyntheti- moval, conservation ecology and, more broadly, plant science. cally produced oxygen in their leaves to their roots and rhi- zomes (Borum et al., 2006), thereby maintaining a protective Can we improve photosynthesis? oxidized layer a few millimeters thick around their roots and rhizomes (Brodersen et al., 2015). Oxygen transport from Photosynthesis: A key target for improving crop photosynthetic production sites to roots is enabled by the productivity, sustainability, and resilience in the development of a lacunae system that provides gaseous con- face of climate change nectivity between leaves, rhizomes, and roots (Borum et al., (By Elizabeth A. Ainsworth and Andrew D.B. Leakey) 2006). While continuous within organs, they are interrupted Photosynthesis heavily influences crop productivity, resource between organs by diaphragms one cell thick, perforated by use efficiency, and sensitivity to stresses. Therefore, strategic interstitial pores (0.5–1.0 lm), which provide protection engineering of photosynthetic metabolism and the morpho- from flooding while allowing gas flow (Roberts et al., 1984). logical features of leaves that control carbon and water In addition, the below-ground tissues of seagrasses exhibit fluxes can: (1) increase the food, fuel, fiber, and feed pro- physiological adaptations which allow them to rely tempo- duced by crops; while (2) reducing demand for water and rarily on anaerobic fermentative metabolism (Borum et al., improving agricultural GHG balance; and (3) making crops 2006). more resilient to future climatic and atmospheric conditions. Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 33 Detailed models of photosynthetic metabolism (Zhu et al., recycles 2P-glycolate at the expense of ATP and NADH 2012; Bellasio, 2019) and crop function can identify engi- (Walker et al., 2016). A number of genetic engineering strat- neering strategies (Kromdijk et al., 2016; Leakey et al., 2019; egies have successfully demonstrated that photorespiration Wu et al., 2019). Synthetic biology is also opening doors for can be partially bypassed, resulting in improved photosyn- novel photosynthetic systems to be custom designed to thetic carbon assimilation (Kebeish et al., 2007; Carvalho new environments (Zhu et al., 2020, and discussed below by et al., 2012; South et al., 2019). Recently, transgenic tobacco Lu and Liao). Here, we discuss engineering for greater photo- (Nicotiana tabacum) was developed to recycle 2P-glycolate synthesis under near-future elevated atmospheric CO2 con- in the chloroplast via overexpression of plant malate syn- centrations and temperatures, plus improved thase and Chlamydomonas (C. reinhardtii) glycolate dehy- photosynthetic water use efficiency (WUE) and NUE. drogenase and simultaneous RNAi to downregulate a Despite a general effect of higher atmospheric CO2 en- glycolate–glycerate transporter (South et al., 2019). When hancing photosynthesis in C3 plants, global warming is these plants were grown in the field at elevated tempera- expected to have profoundly negative consequences for crop tures ( + 5C), they showed greater resilience to heat stress photosynthesis and productivity by the middle to end of this compared to wild-type (Cavanagh et al., 2022), providing century (Slattery and Ort, 2019). Rising temperatures also in- strong proof-of-concept for this strategy. crease vapor pressure deficit (Ficklin and Novick, 2017), Growth at elevated CO2 (550–600 ppb, which is in the which may increase irrigation demand in the future and limit range of predicted average atmospheric CO2 concentrations the potential yield of current crop genotypes grown under by 2050) generally enhances yields of C3 crops in major tem- standard management practices (Ort and Long, 2014; perate growing regions (Ainsworth and Long, 2021). This pri- DeLucia et al., 2019). Photosynthesis is a temperature- marily results from enhanced photosynthetic CO2 fixation dependent process, with rates increasing to an optimum, driven by greater Rubisco carboxylation rates combined then decreasing once that temperature optimum is exceeded with inhibition of Rubisco oxygenation rates (Stitt, 1991). (Moore et al., 2021). This temperature dependency reflects Even if C3 plants acclimate to elevated CO2 in the long term the biochemical processes that determine rate limitations, by downregulating investment in Rubisco content and elec- namely Rubisco activity (and the balance between photosyn- tron transport capacity, photosynthesis is generally stimu- thetic carbon assimilation and photorespiration) and lated along with NUE (Leakey et al., 2009). Field experiments ribulose-1,5-bisphosphate regeneration. While in vitro with transgenic plants overexpressing Calvin–Benson– Rubisco carboxylation rates increase beyond 50C, de- Bassham (CBB) cycle enzymes further enhanced the benefits creased discrimination by Rubisco for oxygen and increased of elevated CO2 on carbon gain and yield by increasing pho- solubility of oxygen relative to CO2 with rising temperatures tosynthetic electron transport capacity (Rosenthal et al., inhibit net photosynthetic carbon assimilation in temperate 2011; Köhler et al., 2017). If coupled with breeding or engi- C3 crops at temperatures exceeding 30C, due to increased neering to maintain high sink capacity, which is a prerequi- photorespiration (Moore et al., 2021). Rubisco activase is a site to maximizing the potential of photosynthetic key target for improving photosynthesis at elevated tempera- enhancements in elevated CO2 (Ainsworth and Long, 2021), tures because of the thermolability of the enzyme (Salvucchi this provides a widely applicable pathway to a greater CO2- and Crafts-Brandner, 2004) and the observation that acti- fertilization effect on yield. vases from species or genotypes adapted to warmer climates Greater atmospheric CO2 also causes stomatal closure, are more thermostable (Scafaro et al., 2016). resulting in lower transpiration and greater WUE (Leakey Work in Arabidopsis thaliana suggested that simply over- et al., 2009, 2019). This can reduce drought-induced stress expressing a thermostable Rubisco activase could improve and yield loss (Fitzgerald et al., 2016). However, interactions photosynthesis and growth in high temperature conditions with abscisic acid signaling, canopy micrometeorology, and (Kurek et al., 2007), but that result was not translated to N fixation can also cause the CO2-fertilization effect on yield crops where overexpression of Rubisco activase resulted in to be lost under hot and dry conditions (Gray et al., 2016). lower Rubisco content (Fukayama et al., 2012, 2018). Studies There is also significant uncertainty about which of these in rice discovered that over-expression of both Rubisco and responses will occur in tropical locations where water avail- Rubisco activase were required for enhanced photosynthesis ability, high temperatures, and soil fertility might be most at both optimal and high temperatures (Qu et al., 2021; limiting (Leakey et al., 2012). A possible target to improve Suganami et al., 2021). A highly thermostable Rubisco acti- yield in times and places of drought is to reduce the vase identified in the Crassulacean acid metabolism plant amount of water lost through stomata to the atmosphere Agave tequilana (Shivhare and Mueller-Cajar, 2017) and relative to photosynthetic CO2 uptake, that is increasing greater understanding of the mechanisms of thermostability WUE by reducing stomatal density or accelerating stomatal in different Rubisco activase isoforms (Scafaro et al., 2019; closing speed (Leakey et al., 2019). Modeling suggests that Degen et al., 2020) provide potential guides for further im- prioritizing reductions in water use over increases in carbon proving thermotolerance in crops. gain when trying to enhance WUE may lead to better yield Another target for improving photosynthesis at elevated outcomes in many growing environments for both C3 and temperatures is reducing photorespiration, the process that C4 species, especially as atmospheric CO2 concentrations Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 34 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. continue to rise (Leakey et al., 2019; Wu et al., 2019). studies (South et al., 2019). When GO was replaced with Successful pursuit of this strategy would increase productiv- Chlamydomonas glycolate dehydrogenase (GDH), which ity while making currently marginal land viable for produc- produces NADH instead of H2O2, transgenic tobacco tion, reduce freshwater use for irrigation, and make crops showed higher carbon assimilation rates, resistance to pho- more resilient to climate change. torespiration stress, and a significant increase in biomass in Crop productivity today is highly dependent on fertilizer the field tests (South et al., 2019). Under high temperatures application, which has negative environmental effects ( + 5C), this pathway decreased yield loss by 11%–21% through nitrate run-off and release of the potent GHG ni- (Cavanagh et al., 2022). trous oxide. The need for N inputs is strongly linked to the high N cost of photosynthetic proteins. However, there may Conversion of two glycolate (C2) to one glycerate (C3) with be potential to re-invest N in different photosynthetic com- CO2 release in chloroplasts (Figure 4B). The synthetic path- ponents to increase carbon gain and improve NUE (Evans way originated from E. coli, consisting of dehydrogenase and Clarke, 2019). (GDH), glyoxylate carboligase (GCL), and tartronic semialde- hyde reductase (TSR). Unlike the first approach, this syn- Enhancing plant CO thetic pathway preserves 75% of carbon from two glyoxylate 2 fixation through synthetic biology to produce one glycerate, which is returned to the CBB cy- (By Kuan-Jen Lu and James C. Liao) cle (Kebeish et al., 2007). The remaining carbon is CO2 pro- duced via GCL. Expressing the above genes in Arabidopsis Synthetic biology encompasses engineering natural or non- chloroplasts increased the growth rate and biomass yield. natural enzymes or pathways into plants to accomplish a This synthetic pathway was shown to benefit crop plants designated purpose. In addition to the approaches discussed such as Camelina sativa and potato (Solanum tuberosum) in above, here we discuss attempts using synthetic biology to greenhouse and growth chamber conditions (Nolke et al., enhance CO2 fixation, focusing on recycling photorespiration 2014; Dalal et al., 2015). products and CO2-fixation pathways (Figure 4). Fixation of an additional CO2 to compensate for the carbon Recycling photorespiration products loss by GCL (Figure 4C). The synthetic malyl-CoA glycerate Plant photorespiration produces a nonproductive product, (MCG) cycle also uses GCL, and TSR to convert two glyoxy- 2P-glycolate, through the oxygenase activity of Rubisco. 2P- lates to glycerate, which is then converted to phosphoenol- glycolate is converted to glycerate in peroxisomes and to phyruvate (PEP). The oxygen-insensitive PEP carboxylase CO2 in mitochondria in a process requiring ATP and (PPC) then carboxylates CO2 and PEP to OAA (C4), fol- NADPH with CO2 and ammonium released (Walker et al., lowed by splitting OAA to acetyl-CoA and glyoxylate (Yu 2016). Current synthetic pathways for reducing photorespir- et al., 2018b). The glyoxylate is then recycled in the GCL re- atory CO2 loss involve the following types: action. The net result is the conversion of glyoxylate (or gly- colate) to a productive biosynthetic product, acetyl-CoA, Breakdown of one glycolate (a C2 compound) to two CO2 in without carbon loss. The MCG cycle has been accomplished chloroplasts without ATP or NADPH consumption (Figure in Synechococcus elongatus PCC7942, a photoautotrophic cy- 4A). The released CO2 can be reassimilated by Rubisco, and anobacterium (Yu et al., 2018b). Compared to the wild-type, no ammonium would be released. For example, an engi- the strain expressing the MCG cycle fixed higher amounts of neered “GOC” pathway in rice consists of a glycolate oxidase CO (OsGLO3), an oxalate oxidase (OsOXO3), and a catalase 2 to produce more acetyl-CoA and its derived compound ketoisocaproate, an intermediate in leucine biosynthesis. (OsCATC) overexpressed in rice chloroplasts (Shen et al., 2019). Glycolate is converted to oxalate, which is completely Fixation of an additional CO2 to glycolate after activation oxidized to two CO2 by OsOXO3. OsCATC is required for (Figure 4D). An elegant tartronyl-CoA (TaCo) pathway was decomposing H2O2, preventing plants from oxidative stress. demonstrated recently, in which glycolate is activated to Rice plants engineered with the GOC pathway showed a glycoly-CoA, which is then caboxylated to tartronyl-CoA 22% increase in photosynthesis, but increases in yield were and then to glycerate. This approach requires a new-to- inconsistent and dependent on the season in field tests nature enzyme, glycolyl-CoA carboxylase, which was devel- (Shen et al., 2019). An earlier example overexpressed a ma- oped by rational design and high-throughput screening late synthase (MS) from pumpkin (Cucurbita pepo), a cata- (Scheffen et al., 2021). lase (CAT) from Escherichia coli, and a peroxisomal glycolate oxidase (GO) in Arabidopsis chloroplasts (Maier et al., 2012). Rubisco-independent, synthetic CO2 fixation pathways In this manner, glycolate is completely oxidized to CO2 via Six Rubisco-independent CO2-fixation pathways in microor- both the heterologous and endogenous enzymes. The trans- ganisms have been identified in nature (Berg, 2011), and a genic Arabidopsis had a greater rosette number and size number of theoretical synthetic pathways have been with higher biomass under the ambient CO2, short-day con- designed in silico based on reported enzyme activities and ditions. However, introduction of the above three genes in thermodynamics (Bar-Even, 2018). The first step in imple- tobacco did not result in increased biomass in greenhouse menting synthetic pathways is to demonstrate the pathway Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 35 Figure 4 Synthetic biology approaches for recycling photorespiration and CO2-fixation pathways. A and B, Photorespiration engineered for break- down of one glycolate to two CO2 molecules (A) or conversion of two glycolate to one glycerate plus one CO2 molecule (B). The CO2 released in the chloroplast is recycled back to the CBB cycle for carbon reassimilation (Maier et al., 2012; Shen et al., 2019; South et al., 2019). C, The MCG-cy- cle engineered to convert glycolate to acetyl-CoA without carbon loss (Yu et al., 2018b). D, Creation of a new enzyme, such as glycolyl-CoA car- boxylase, to achieve glycolate recycling to produce glycerate with input of ATP and an additional CO2 molecule (Scheffen et al., 2021). E, Rubisco- independent CETCH and rPS-MCG synthetic CO2-fixation pathways (Luo et al., 2022). feasibility in a cell-free system. This in vitro demonstration export any of its intermediates as a product, such as acetyl- requires in-depth processes in solving problems in co-factor CoA (C2), pyruvate (C3), and malate (C4). This self- regeneration, enzyme stability, and pathway control. replenishing characteristic is also seen in almost all naturally Through these processes, incompatibility of enzyme reac- evolved cycles. Since the output C2, C3, or C4 intermediates tions, kinetic barrier, and thermodynamic limitations can be are essential for cell growth, it is potentially malleable for identified. To date, two Rubisco-independent synthetic CO2- in vivo engineering. Introduction of the CETCH cycle or the fixing pathways, CETCH and reductive pyruvate synthesis rPS–MCG cycle in a plant would require the activity of (rPS)–MCG (Figure 4E), have been demonstrated, and many heterologous enzymes, along with co-enzyme B12, achieved similar or increased CO2 fixation rates in vitro which is absent in plants. Hence, enzyme design, pathway compared with the CBB cycle in vivo (Schwander et al., evaluation in prokaryotes, plant-associated microbiome engi- 2016; Luo et al., 2022). The CETCH pathway consists of 17 neering, and various genome editing strategies have been enzymes from different organisms (Schwander et al., 2016). proposed to facilitate this process (Erb et al., 2017; Gupta An oxygen-insensitive carboxylase/reductase (CCR) from et al., 2021; Ke et al., 2021). Methylorubrum extorqens was chosen as the carboxylase to fix CO2 in the CETCH cycle because of its high carboxylase Engineering carbon dioxide-responsive C3 crops to activity and broad substrate range. The carboxylation sub- sustain higher productivity under a CO2-rich, strate acrylyl-CoA and crotonyl-CoA in CETCH were regen- warmer climate erated to complete the cycle for continuous fixation of CO2. (By Rajeev N. Bahuguna and S. V. Krishna Jagadish) The fixed carbon is converted to glyoxylate as the output. C4 plant species are overrepresented in agriculture systems The rPS–MCG cycle consists of two parts (Luo et al., and have substantially higher productivity compared to C3 2022). The first utilizes the MCG cycle described above. In crops mainly due to higher photosynthetic efficiency (Rao the second part, rPS converts acetyl-CoA to pyruvate et al., 2012; Sales et al., 2021). Yet a number of C3 crops are through a series of reactions that takes two acetyl-CoA to important food sources for millions of people globally, in- make a crotonyl-CoA, which is carboxylated by CCR to pro- cluding cereals such as wheat, rice, barley (Hordeum vulgare), duce a C5 compound. The C5 compound is split into a C3 oats (Avena sativa), and many vegetable and tree crops. (pyruvate) and C2 (acetyl-CoA) through a series of carbon Therefore, efforts to increase the photosynthetic efficiency rearrangement reactions that complete the cycle. The rPS– and productivity of C3 crops are underway to help meet the MCG cycle exhibits a self-replenishing feature as it can increasing global food demand (Cui 2021). The high CO2 Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 36 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. saturation point for photosynthesis of C3 plants (intercellu- on RN have been reported, ranging from direct inhibition of lar CO2 levels 600 mmol mol–1) makes them more respon- respiration to no significant impact or even an increase un- sive to elevated CO2 than C4 plants, which are saturated for der long-term exposure to elevated CO2 (Griffin et al., 1996; CO2 under current atmospheric CO2 levels (Loladze, 2014; Gonzalez-Meler et al., 1996, 2004; Ziska and Bunce, 1998; Dingkuhn et al., 2020; Kundu et al., 2022). Thus, C3 crops Drake et al., 1999; Baker et al., 2000; Davey et al., 2004; Ayub provide a unique opportunity to harvest more carbon from et al., 2014). However, none of these studies considered the a CO2-rich environment and convert it to biomass and yield genetic background for CO2 responsiveness, which could be (Broberg et al., 2019; Ainsworth and Long, 2021). a major determinant of the effect of elevated CO2 on RN, In contrast to the positive effect of CO2 on C3 photosyn- and carbon balance dynamics in C3 crops (Figure 5). thesis, the global rise in temperature is a major factor limit- Despite the well-documented photosynthetic enhance- ing the yield of major cereal crops (Lobell and Gourdji, 2012; ment of C3 crops under elevated CO2 (Leakey et al., 2009), Teixeira et al., 2013; Zhao et al., 2017). A rise in night tem- active selection in C3 crops for CO2 responsiveness has not perature has been shown to have a large impact on the pro- been given adequate attention (Ziska et al., 2012; Dingkuhn ductivity of C3 crops such as rice (Peng et al., 2004; Welch et al., 2020). The complexity of field-based CO2 enrichment et al., 2010) and wheat (Hein et al., 2020, 2022; Impa et al., facilities and space constraints for screening and characteriz- 2021). Recent studies suggest that high night temperature ing a large number of genotypes remain major bottlenecks (HNT) is related to physiological changes such as an in- for identifying potential CO2-responsive genotypes. Recently, creased rate of night respiration (RN) and a reduced rate of Shimono et al. (2014) and Kikuchi et al. (2017) demon- starch accumulation in developing grains in rice (Bahuguna strated that altering planting density provides a means of et al., 2017; Shi et al., 2017), wheat (Narayanan et al., 2016a, assessing phenotypic plasticity in rice genotypes under en- 2016b; Impa et al., 2020), and barley (Garcıa et al., 2015, hanced resource availability (e.g. space, light, nutrients). 2016). Hence, the positive effect of CO2 on C3 photosynthe- Interestingly, genotypes responsive to higher available sis and augmented rate of night respiration under HNT resources under low planting density responded similarly have opposing effects on carbon-balance dynamics under under an elevated CO2 environment (Shimono et al., 2014). CO2-rich, warmer environments (Song et al., 2014; Dusenge Subsequently, in a series of field experiments, Bahuguna et al., 2019). While the sensitivity of RN to a rise in tempera- et al. (2022) assessed the variable phenotypic plasticity of ture is well documented (Atkin and Tjoelker, 2003), variable 194 diverse rice genotypes by measuring parameters related effects of the long- and short-term impact of elevated CO2 to photosynthesis, biomass, and yield under different Figure 5 Schematic diagram showing average annual atmospheric [CO2] level for 2021 and the effect of rising night temperature (Tmin) on rice productivity by enhanced respiration: photosynthesis ratio (RN/A) resulting in augmented release of carbon at the cost of biomass and yield in conventional genotypes. On the contrary, introgression of CO2-responsiveness trait in C3 crops facilitates enhanced carbon sequestration and allo- cation of additional carbon into biomass, and compensating Tmin-induced carbon losses. LCR, least CO2-responsive; HCR, high CO2-responsive. Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 37 planting densities. A wide genetic variability observed for four-carbon reaction product subsequently transported to the phenotypic plasticity under a resource-rich environment inner bundle sheath cells for decarboxylation and re-fixation showed a strong relationship (R2 = 0.71) with CO2 respon- by Rubisco in the Calvin cycle (Figure 6). Given the special- siveness under realistic CO2 conditions using a field-based ized leaf anatomy and compartmentalization of metabolic free air CO2 enrichment facility. Further, the high CO2-re- reactions required for C4 function, evolution of the pathway sponsive (HCR) genotypes showed significantly higher rates must have involved functional modification of multiple of photosynthesis (A) and lower rates of RN resulting in a genes, including those encoding enzymes, metabolite trans- lower RN/A ratio as compared to the least CO2-responsive porters, and regulators of cell-type patterning. Despite this (LCR) genotypes. Interestingly, elevated CO2 was identified apparent complexity, the C4 photosynthetic pathway as the major driver influencing carbon-balance dynamics evolved over 60 times independently and is represented in and the phenotypic response of HCR genotypes resulting in diverse families of flowering plants (Sage, 2016). The adap- higher biomass and yield under elevated CO2 + HNT condi- tive success of the C4 photosynthetic strategy is demon- tions, whereas the LCR genotype was severely affected by strated by the fact that just 2% of plant species utilize the HNT despite exposure to elevated CO2. pathway but C4 plants are responsible for 25% of terres- This study demonstrated that the impact of HNT on grain trial primary productivity (Still et al., 2003). yield, total biomass, and grain weight was compensated by elevated CO2, but this response was mainly confined to the Why C4 rice? HCR genotypes (Bahuguna et al., 2022). Thus, LCR or con- In addition to strategies that aim to improve the efficiency ventional genotypes are expected to lose biomass and yield of the C3 photosynthetic pathway (discussed above, and see under an elevated CO2, warmer climate due to augmented Ort et al., 2015; Johnson, 2022) or to introduce Crassulacean respiratory carbon losses, whereas HCR genotypes could ac- acid metabolism into C3 plants (Schiller and Bräutigam, cumulate more carbon per unit area and maintain their bio- 2021), the enhanced efficiency of C4 photosynthesis provides mass and yield by compensating for carbon losses under a potential engineering opportunity for improved yield and HNT (Figure 5). In addition, the ability to fix additional car- resilience against abiotic stresses in C3 crops. Although the bon with a lower respiration-to-photosynthesis ratio in HCR C4 pathway utilizes two extra ATP molecules per CO2 fixed genotypes provides an opportunity to sequester a substan- than the C3 pathway, in warm and dry environments where tial amount of carbon into biomass. There is, however, a dissolved oxygen conditions are relatively high, these energy need for prediction models for simulated carbon fluxes at costs are offset by those not spent on photorespiration (3.5 temporal and spatial scales to assess the carbon sequestra- ATP per O2 fixed). In general, C4 plants also use less water tion potential of CO2-responsive C3 crops. In conclusion, the (Kocacinar et al., 2008) and N (Evans and von Caemmerer, introgression of a ‘CO2-responsiveness’ trait into elite rice va- 2000) per CO2 fixed and have substantially faster growth rieties and other C3 crops could help sustain and enhance rates (Monteith 1978). Physiological models that incorporate crop yield in a warmer environment. these factors predict that if C4 traits could be introduced into C3 plants, enhanced radiation, N, and WUEs could gen- The C4 rice project erate substantial yield increases, particularly in warm envi- (By Jane Langdale) ronments where crops are rainfed and fertilizer applications In the majority of photosynthetic organisms, both in water are limited (Mitchell and Sheehy, 2006). and on land, CO2 is fixed by Rubisco into the three-carbon Importantly, the level of atmospheric CO2 at which C4 compound 3-phospho-glycerate, the first intermediate of outcompetes C3 is dependent on temperature; C4 is favored the CBB cycle. The efficiency of this C3 photosynthetic path- below 550 ppm CO2 at 35C, 450 ppm at 30C, and 350 way is compromised because Rubisco also reacts with oxy- ppm at 25C (Ehleringer et al., 1997). Although future pre- gen, forming 2-phospho-glycolate, which has to be dictions of atmospheric CO2 levels differ depending on fossil detoxified in the energetically costly photorespiratory path- fuel usage scenarios, with current levels at 419 ppm and an- way (Walker et al., 2016). Because of this energetically waste- nual increases of 2–3 ppm over the last decade (https://gml. ful competitive reaction, the decrease in atmospheric CO2 noaa.gov/ccgg/trends/gl_gr.html), the status quo would re- levels that occurred during the Oligocene (Pearson et al., sult in atmospheric CO2 levels of 500 ppm by 2050. C4 2009) would have been accompanied by photosynthetic in- plants could thus outperform C3 plants where temperatures efficiencies at a global scale. exceeded 33oC, which given climate warming predictions The reported drop from 800 to 400 ppm atmospheric could be much of the global agricultural landscape for at CO2 during this period is thought to have driven, at least in least part of the year. Leaving predictions aside, long-term part, the evolution of the C4 photosynthetic pathway that field experiments at elevated ( + 180 ppm) CO2 demon- concentrates CO2 at the site of Rubisco and thus minimizes strated that the biomass of C3 but not C4 grasses was en- photorespiration (Sage, 2016). In the C4 pathway, CO2 is ini- hanced over the first 12 years of the project but then C4 tially fixed by phosphoenolpyruvate carboxylase (PEPCase), outperformed C3 in the following 8 years (Reich et al., 2018). which is oxygen insensitive. This carboxylation reaction This switch was correlated with net N mineralization rates occurs in the outer mesophyll cells of the leaf, with the in the soil, which were initially enhanced by elevated CO2 in Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 38 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. Figure 6 Schematics of C3 CBB and NADP-ME C4 Cycles. A, CBB C3 cycle. B, NADP-ME C4 cycle. C, Transverse leaf sections and corresponding schematics of C3 rice (left) and C4 maize (right). Bars = 30 lm. Adapted from Langdale (2011), Figures 1 and 3. C3 plots but were later depressed. Despite the difficulties in of the genes encoding metabolite transporters (reviewed in predicting exactly how plants will respond to global change, Langdale, 2011), but regulators of C4 leaf anatomy had not C4 engineering is thus a plausible strategy, albeit one with been identified. The strategy to introduce C4 traits into rice significant challenges. was thus three-pronged: (1) introduce compartmentalized C4 metabolism into existing bundle sheath cells and the Strategy mesophyll cells immediately adjacent to them by expressing The C3 species rice is an obvious target for C4 engineering maize genes in specific cell-types of rice; (2) activate chloro- because it is one of the world’s top three staple crops and plast development and photosynthesis in existing bundle in many parts of Asia it is the major source of calorie intake. sheath cells by expressing a known regulator of chloroplast With predicted population increases, the one hectare of development in maize (the Golden2 [ZmG2] gene; Hall land that provided enough rice to feed 27 people in Asia in et al., 1998); and (3) identify regulators of C4 leaf anatomy 2007 will need to support at least 43 people by 2050—a in maize with a view to future manipulation in rice. The 60% increase in demand (Zeigler, 2007). Successful conver- ultimate goal was to combine the metabolic prototypes sion of a C3 plant into one that utilizes the C4 pathway generated in the first two strands with the anatomical requires that leaf anatomy be modified to reduce the num- prototype. ber of mesophyll cells between veins to the extent that Much of the first decade of the project was spent devel- there is an approximate 1:1 ratio of mesophyll:bundle sheath oping tools in rice to enable this strategy, for example ro- cells in the leaf; that chloroplast development is activated in bust transformation pipelines, cell-type-specific promoters, the normally achlorophyllous bundle sheath cells; and that and modular cloning technology. Ongoing research contin- C4 pathway enzymes and metabolite transporters are com- ues to characterize potential regulators of C4 leaf anatomy partmentalized and functional in either the mesophyll or and to evaluate whether manipulation in rice can modify bundle sheath cells. cell-type patterning in the leaf (Wang et al., 2013a, 2017a; When the C4 Rice Project (www.c4rice.com) was initiated, Schuler et al., 2018; Hughes et al., 2019; Hughes and genes encoding all of the enzymes of the C4 pathway had Langdale, 2020, 2022)—but much more discovery research is been identified in maize and other C4 species, as had some needed before an anatomical prototype can be designed Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 39 and engineered (Sedelnikova et al., 2018). Recent work has, introgression of single genes/QTLs. With a few exceptions however, made progress toward engineering C4 metabolic (i.e. Sub1 varieties for submergence such as Swarna-sub1 prototypes. [Mackill et al., 2012] and drought-tolerant DRR dhan 42 [IR64 qDTY2.2 + qDTY4.1; Swamy et al. 2013]) the majority Progress of recently released stress-tolerant varieties were convention- Maize genes encoding C4 pathway enzymes have been ally bred (i.e. by crossing and selecting over several expressed in specific cell types of both an elite cultivar of generations). indica rice (IR64) and a model cultivar of japonica rice The use of genes and QTLs through marker-assisted selec- (Kitaake), and in both cases the pathway is partly functional. tion could shorten the breeding process. Although hundreds Specifically, primary carboxylation by PEPCase is seen in me- of stress-tolerance genes, QTLs, and physiological mecha- sophyll cells, but subsequent decarboxylation in bundle nisms have been identified, only a small number of these re- sheath cells has yet to be detected (Lin et al., 2020; search outputs have been used in breeding (Wissuwa et al., Ermakova et al., 2021). Creating a fully functional cycle will 2016; Cobb et al., 2019; Platten et al., 2019) and the fre- require a better understanding of metabolite flux within and quency of known abiotic stress QTLs in the current elite between the two cell types, which may require the develop- breeding material remains low (Juma et al., 2021). There is ment of more sensitive detection methods. In a second ad- thus a need to bridge the gap between upstream science vance, chloroplast development has been activated in the and breeding for adaptation to climate change so that valu- normally achlorophyllous bundle sheath cells of rice, able traits/genes/QTLs are more actively utilized in breeding through constitutive expression of ZmG2 (Wang et al., pipelines. 2017b). No fitness penalty was observed in greenhouse- Modern breeding strategies have shifted to a paradigm of grown lines expressing ZmG2, in either IR64 or Kitaake back- population improvement based on elite x elite crossing grounds (Wang et al., 2017b) and although only evaluated (Juma et al., 2021) within core panels, which for stress-prone in the nonelite Kitaake background, field-grown lines overex- areas have been selected from the most stress-tolerant geno- pressing ZmG2 exhibited up to 30% yield increases (Li et al., types available (i.e. Khanna et al., 2022). This strategy 2020). These examples validate the overall engineering strat- presents significant opportunities for upstream plant biolo- egy but there is still a long way to go before a full transition gists to contribute to breeding efforts. With a defined list of to C4 can be achieved in any C3 species. genetic backgrounds (many of which have already been se- Can we develop climate-resilient crops? quenced; see, for example, Mansueto et al., 2017) to which potential stress tolerance traits/genes/QTLs can be com- The trait development pipeline: Bridging the gap pared, those that best complement the elite breeding pool between upstream science and breeding for can be prioritized. However, although traditional varieties adaptation to climate change are the most promising source of stress tolerance, they also (By J. Damien Platten and Amelia Henry) typically possess detrimental traits that make them unsuit- Improving the adaptability of crops is a key strategy to miti- able for use in elite  elite crossing. A defined protocol is gate the effects of climate change on productivity (Aggarwal needed to deliver useful traits/genes/QTLs from traditional et al., 2019). We focus on rice breeding in this section; how- varieties into elite backgrounds and into the breeding pool. ever, the pipeline we describe (Figure 7) could easily be ex- In seeking to bridge the gap between upstream plant sci- tended to other crops, taking into consideration the ence and breeding for stress tolerance, an understanding of challenges and parameters unique to each species. For ex- breeding program needs is critical. In the briefest terms, reli- ample, the platform is being adopted across the CGIAR ability is key: a gene/QTL must reliably improve the target partnership for global food security (https://www.cgiar.org/) trait, in relevant elite genomic backgrounds and in relevant for other mandate crops. In rice breeding, abiotic stress tol- environments (field locations). Therefore, the growth stages, erance was not a selection target during the Green genetic backgrounds, and environmental conditions relevant Revolution, and some evidence suggests that stress tolerance to breeding programs should be reflected in the study sys- was even selected against due to tight linkage between tems used in upstream research. One example is in the vali- stress tolerance loci and loci conferring unfavorable agro- dation of candidate genes for stress tolerance: this is nomic traits (Vikram et al., 2015). Subsequently, a range of frequently done in the background of japonica rice due to breeding approaches has been taken to improve stress toler- the established transformation protocols. However, the rice ance, including introgression of quantitative trait loci (QTLs) type preferred in most stress-prone rice-growing regions is for stress tolerance traits as well as direct selection for grain indica, which grows better than temperate japonica rice in yield under stress using traditional varieties as the sources of field trials in the tropics. Use of the relevant genetic back- stress tolerance. Characterization of stress-tolerant varieties ground is important because stress tolerance alleles are of- has revealed that combinations of physiological traits have ten absent in japonica genomes and thus their level of stress been affected by selection for yield under stress (Anantha tolerance is more easily improved, exaggerating apparent ef- et al., 2016; Kumar et al., 2021), which may explain some of fect size. Other recommendations for increasing the likeli- the difficulty in developing superior varieties through hood of upstream research outputs being taken up by Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 40 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. Figure 7 The Trait Development Pipeline for delivery of valuable stress tolerance traits/genes/QTLs from upstream research into the elite breeding pool for improvement of crop productivity under climate change. The Trait Development Pipeline is organized into six stages: 1) guidelines for prioritizing traits (assessment), 2) defining standards for phenotyping protocols, 3) identifying donors and QTL (including refining marker quality metrics), 4) introgressing and 5) validating traits/genes/QTLs into elite genetic backgrounds to develop the elite donor lines that are 6) handed to the breeding program for crossing. Those elite donor lines will then be systematically crossed and tested in target environments where climate change is increasingly affecting the degree of abiotic stress affecting crop production. Created with BioRender.com breeding are to take additional steps such as validation of most recently identified traits/genes/QTLs to incorporate identified QTLs in relevant elite genomic backgrounds and into the breeding program, while at the same time effec- to link with researchers who can evaluate the material under tively connecting with local breeders who can conduct wide- field conditions. spread testing and who understand the needs of farmers in On the other side of the gap, downstream science must stress-prone regions. This “bridge building” among scientific make released varieties and advanced breeding lines more disciplines is critical to the development of more efficient accessible to upstream scientists. Familiarity with this mate- pipelines that bring novel improvements to crops for cli- rial is important because in some cases, key genes have been mate change-affected farmers. identified and advocated as promising breeding targets with- To strengthen linkages between upstream and down- out the recognition that they are already present in the stream development efforts, a framework has been devel- breeding pool. Furthermore, the availability of improved ma- oped that organizes and codifies trait development efforts. terial to upstream researchers will help to ensure that target This “Trait Development Pipeline” developed at the loci are effective in those genetic backgrounds. Downstream International Rice Research Institute (Figure 7) applies stage science also must stay up to date and gain access to the gate systems widely used in industry (Covarrubias-Pazaran Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 41 et al., 2022) to assess trait development progress against de- improvement. Breeders have traditionally used CWRs as fined advancement criteria. The organization by stages ena- sources of superior traits, including key traits for enhancing bles external review of the progress at each stage and adaptation to climate change (Dempewolf et al. 2014). The provides decision points on whether to proceed, giving an main breeding objectives for climate change adaptation in- opportunity to discontinue efforts that are not likely to clude resilience to abiotic stresses (drought, heat, salinity, make an impact in breeding programs. and flooding/waterlogging) and biotic stresses brought The current Trait Development Pipeline is organized into about as a result of the increase in atmospheric CO2 and el- six stages that link a variety of research disciplines, and the evated average temperatures. Here, we provide examples of pipeline provides a structure that gives a framework for recent progress in the use of CWRs in managing these teamwork between these areas. The pipeline starts with an stresses and highlight specific areas where work is needed. assessment of the trait of interest in the context of priority Table 1 provides a summary of the use of CWRs in breeding traits needed by farmers and consumers that are not already for tolerance to abiotic stresses. present in the elite breeding pool (see “Product concepts” and “Market segments”; Covarrubias-Pazaran et al., 2022). A Drought stress set of criteria regarding the availability and reliability of phe- Despite the complexity of drought stress (Ilyas et al., 2021), notyping protocols for the trait, potential donor genotypes, CWRs have been reported that are more efficient than crop mapping populations, QTLs, and markers determine ad- relatives in drought-related physiological processes such as vancement to subsequent stages in the Trait Development higher WUE, higher CO2 assimilation, deeper root systems, Pipeline. The pipeline is dynamic and subject to modifica- more efficient regulatory networks, leaf curling, and stomatal tion over time based on researcher feedback and as techni- closure, as well as showing an abundance of allelic diversity ques and technologies change. The outputs of the Trait within candidate genes. For example, higher WUE, higher car- Development Pipeline are validated donor lines containing bon assimilation, and greater carboxylation efficiency were new traits/genes/QTLs in a fully elite background. These reported in wild lettuce (Lactuca serriola; Eriksen et al., 2020), “elite donor lines” can be used in the elite  elite crossing and Moenga et al. (2020) reported novel divergent drought work to improve the most advanced breeding lines which tolerance mechanisms in wild chickpea (Cicer reticulatum) will be evaluated in multilocation trials, evaluated by local that would be a great resource for improving cultivated researchers, and considered for release as varieties for dis- chickpea (Cicer arietinum). Drought-related transcription fac- semination to farmers. In this way, the outputs of trait/ tors of the Asr (abscisic acid, stress, ripening) family have a gene/QTL discovery realize an ongoing impact across the high level of diversity in CWRs (Cortés et al. 2012) that might breeding pool rather than improving just a single variety. be further exploited to improve cultivated crops. Most Such sustained improvement through mainstream breeding drought studies to date in CWRs have focused on major programs will facilitate the deployment of new technologies crops, and there is tremendous scope to undertake similar to as many climate-change-affected crop production market studies in minor and under-researched crops. segments as possible. Application of the pipeline to known genes and QTLs Heat stress helps to identify gaps in knowledge and products available, Heat stress is one of the greatest concerns for crop produc- and addressing these gaps is already enabling the rapid in- tion considering the increasing effects of climate change. troduction of a wide variety of genes contributing to disease The wild wheat relatives Triticum monococcum, T. dicoc- resistance, heat, drought, cold, and salinity tolerance into coides, and Aegilops speltoides ssp. liqustica and CWR- mainstream rice breeding efforts. Breeding programs are derived wheat genotypes were among the most heat toler- thus able to respond in a far more agile manner to changing ant when tested alongside elite wheat genotypes (Peng climate and market demands. As these genes are deployed et al., 2013; El Haddad et al., 2021). Similar observations have into elite backgrounds, it becomes easier for small breeding been made in wild rice, Oryza meridionalis Ng. and O. aus- programs to also leverage their value; the “heavy lifting” of traliensis, in which heat tolerance was associated with a eliminating highly unfavorable genomic backgrounds, break- more stable activation of Rubisco (Scafaro et al., 2016). ing linkage drag, and developing coupling-phase linkages has Overexpressing a thermostable variant of Rubisco activase been done, so only minimal or no additional effort is re- from CWR significantly improved yield in domesticated rice quired to move the new genes to other elite breeding pro- (Oryza sativa L.; Scafaro et al., 2018). More studies on the grams. Thus, the value of new genes is no longer exclusively physiological and molecular basis of heat tolerance in wild available to large, well-resourced programs. versus domesticated species are needed to enhance the de- ployment of novel heat tolerant alleles in crop improvement. Enhancing climate resilience through the use of crop wild relatives Salinity tolerance (By Damaris A. Odeny) Halophytic plants adapt to salinity through three distinct Crop wild relatives (CWRs) are wild species that are closely mechanisms, all of which have been identified in various related to domesticated crops and can be used for crop CWRs: osmotic stress tolerance, Na + or Cl– exclusion, and Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 42 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. Table 1. Examples of wild relatives used to enhance abiotic stress tolerance in cultivated crops Crop More resilient wild species Trait of interest Reference Wheat Aegilops cylindrica Drought Pour-Aboughadareh et al. (2017) Ae. crassa Ae. caudata Triticum urartu T. monococcum Heat Khanna-Chopra and Viswanathan (1999); T. dicoccoides Peng et al. (2013); El Haddad et al. (2021) Ae. speltoides ssp. liqustica T. ararticum Ae. speltoides Salinity Ahmadi et al. (2018) Ae. caudata Ae. cylindrica T. boeoticum Sorghum Sorghum macrospermum Drought Cowan et al. (2020) S. brachypodum Ochieng et al. (2020) S. arundinaceum S. sudanense S. purpureosericeum Banana Musa balbisiana; Drought Eyland et al. (2022) M. acuminata ssp. errans Rice Oryza rufipogon Salinity Tin et al. (2021) O. nivara; O. coarctata Zhang and Xie (2014) O. nivara; O. rufipogon Flooding Niroula et al. (2012) O. meridionalis Ng. Heat Scafaro et al. (2012); Scafaro et al. (2016); O. australiensis Scafaro et al. (2018) Maize Zea nicaraguensis Flooding Mano et al. (2006); Z. luxurians Mano et al. (2005); Z. mays ssp. huehuetenangensis Z. diploperennis Drought Shaibu et al. (2021) Tomato Solanum cheesmaniae; Salinity Dehan and Tal (1978); Shalata and Tal (1998); S. pennellii Mittova et al. (2002); Frary et al. (2010); S. galapagense Pailles et al. (2020) S. pimpinellifolium Heat Driedonks (2018) Tepary bean Wild Phaseolus acutifolius Drought Buitrago-Bitar et al. (2021) Adzuki bean Vigna nakashimae; V. riukiensis Salinity Yoshida et al. (2016) Eggplant Solanum insanum Salinity Brenes et al. 2020) Chickpea Cicer reticulatum Drought Moenga et al. (2020) Sugarcane Saccharum spontaneum Salinity Kasirajan et al. (2021) tolerance of tissue to accumulated Na + or Cl–. Wild rela- can be used to enhance flooding tolerance in elite SUB1 tives of adzuki bean, Vigna nakashimae and V. riukiensis, genotypes, which are not always tolerant to anaerobic con- prevented Na + accumulation in roots and stems, and toler- ditions during germination. Wild species with tolerance to ated accumulated Na + , respectively (Yoshida et al., 2016). A waterlogging/stagnant flooding have been reported to pos- wild relative of tomato, Solanum pennellii, showed greater sess unique alleles for aerenchyma formation (Zhang et al., induction of antioxidant activity than cultivated tomato 2017), or to provide a stronger barrier to radial oxygen loss (Solanum lycopersicum L.) under salt stress (Frary et al., (Pedersen et al., 2021). The availability of these different 2010). Salinity tolerance has also been reported in Oryza gla- sources of flooding/waterlogging resistance in CWRs pro- berrima (Platten et al., 2013), Hordeum spontaneum (Kiani- vides an opportunity to introgress the beneficial alleles into Pouya et al., 2020), and in Aegilops spp. (Zamani Babgohari elite varieties, especially where genomics-assisted introgres- et al., 2013). sion and selection is possible. Flooding tolerance CWRs as sources of resistance/tolerance to biotic stress Flooding tolerance has been mainly studied in rice leading Introgression of disease resistance genes into cultivated crop to the identification of the SUB1 locus (Mackill et al., 2012). species is perhaps the most beneficial use of CWRs in crop Additional submergence-tolerant alleles (SUB1A-1) were improvement to date. Major genes have been introgressed identified from wild rice species O. nivara and O. rufipogon, from CWRs for resistance to late blight (Phytophthora infes- together with a likely presence of other submergence mech- tans) in potato (Solanum tuberosum L.; Ghislain et al., 2019), anisms in other wild rice accessions (Niroula et al., 2012). blast disease (Magnaporthe oryzae) resistance in rice (Yoshida Two anaerobic germination QTLs (qAGP1 and qAGP3) from and Miyashita, 2009) and several other key pathogens in O. nivara introgression lines (Liu et al., 2021a) potentially wheat (Rani et al., 2020) and tomato (Sharlach et al., 2013), Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 43 just to mention a few. Pest resistance also benefited from pathogen pressure (Venkatesh and Kang, 2019). Similarly, CWRs (Therezan et al., 2021), among the most recent being the impact of increased atmospheric CO2 in relation to the introduction of fall armyworm (Spodoptera frugiperda) re- plant–pathogen interactions remains unsettled. For example, sistance from wild relatives of maize (Singh et al., 2022). high CO2 concentrations led to increased susceptibility of Climate change-related warmer average temperatures and al- wheat to fungal infection (Váry et al., 2015), whereas soy- tered weather patterns are contributing to altered patterns in bean (Glycine max) exhibited either enhanced or reduced the occurrence of crop pests and pathogens and the emer- susceptibility to infection, depending on the pathogen stud- gence of new pests and pathogens around the globe, as ex- ied (Eastburn et al., 2010). Deeper insight into the complex plored in more detail in the section by Rim et al. below. More interplay among abiotic and biotic stresses will inform ongo- studies will be needed to focus on the introgression of quanti- ing work to mitigate crop damage caused by extreme cli- tative resistance from wild to cultivated species to improve mate conditions or pathogens. the durability of resistance to various diseases and pests. One mitigation strategy is the application of beneficial microbes that enhance plant health and immunity. For in- De novo domestication for resilience to climate change stance, Actinobacteria in the genus Streptomyces are enriched Despite several wild relatives having remarkable tolerance to in the root microbiome of plants under drought stress biotic and abiotic stresses, successful introgression of these (Naylor et al., 2017). Application of Streptomyces strains to traits into elite backgrounds has been difficult due to linkage seeds improved wheat growth and yield in drought field con- drag (Nevo and Chen, 2010) and the complexity of most ditions (Yandigeri et al., 2012). Beneficial strains of traits. De novo domestication, the incorporation of domesti- Trichoderma fungus heightened plant immunity and antago- cated genes into the nondomesticated species to develop nized pathogenic fungi (Tyskiewicz et al., 2022). Soil applica- new crops (Razzaq et al., 2021), presents a novel opportu- tion of Trichoderma reduced fungal infection in soybeans, nity for immediate utilization of the novel resilience alleles tomatoes, peanuts (Arachis hypogaea), and other crops (Zin in CWRs. The availability of vast genomic and phenomic and Badaluddin, 2020). Inoculation with Trichoderma has resources allow for machine learning (Niazian and Niedbała, also been shown to enhance tolerance to abiotic stresses 2020) and more precise genome editing (Hua et al., 2019). An excellent example of de novo domestication has been such as drought and salinity (Zhang et al., 2016; Scudeletti reported in Solanum pimpinellifolium (Zsögön et al., 2018). et al., 2021). Biocontrol strategies present an opportunity to There are now several countries that have exempted enhance resilience to environmental stress and disease pres- genome-edited plants from genetically modified organism sure, while reducing the use of chemical pesticides or fertil- regulations, making it possible to utilize de novo domesti- izers that can further damage the environment. cated plants as soon as they are generated. Another strategy well-aligned with sustainable agriculture practices is the introduction of genetic improvements that Development of disease-resistant crops for a protect crops against pathogens and confer resilience to abi- changing climate otic stress in a heritable manner. There are numerous exam- (By Ellen Youngsoo Rim, Alexandra M. Shigenaga, Pamela ples of genetic alterations in crops leading to resistance to C. Ronald) specific pathogens, many of which were achieved through the introduction of immune receptors (Ercoli et al., 2022). Plant reactions to a single stress differs from those of plants Immune receptors are activated by direct or indirect interac- exposed to combined abiotic and biotic stresses, with a shift in signaling pathways and transcriptomic responses (Atkinson tion with microbial molecules to elicit host defense and Urwin, 2012; Prasch and Sonnewald, 2013; Sharma et al., responses. Advances in genome sequencing and analysis 2013). Thus, understanding how plants respond to pathogen have accelerated the discovery of immune receptors and stress under nonoptimal environmental conditions is essential other beneficial genetic traits in cultivated crop varieties and for the development of resilient crops in a changing climate their wild relatives (Ercoli et al., 2022; Zsögön et al., 2022; (Chaloner et al., 2021; Velásquez et al., 2018). and discussed in the section above by Odeny). For instance, Diverse plant–pathogen interactions have been shown to a previously unknown variant of the immune receptor FLS2 be affected by adverse environmental conditions, leading to was identified in the genome of a wild grape species (Vitis increased host susceptibility, or in some cases, increased riparia; Fürst et al., 2020). The introduction of the new FLS2 host resistance (Velásquez et al., 2018). Various plant species variant conferred resistance to Agrobacterium tumefaciens in become more susceptible to fungal, viral, or bacterial patho- tobacco, offering a potential strategy to control crown gall gens in response to elevated temperatures (Cohen and disease, which affects many crops including nut trees and Leach, 2020; Velásquez et al., 2018). For example, exposure grapevines. Once identified, desirable genetic traits can be to elevated temperature combined with drought stress led introduced into crops through methods such as marker- to greater susceptibility to Turnip mosaic virus due to down- assisted breeding or genetic engineering. The use of gene- regulated defense response gene expression (Prasch and stacking to introduce multiple protective genes into a single Sonnewald, 2013). However, there are examples where high background will likely be an important consideration in en- temperatures led to enhanced host resistance against gineering climate resilience (Figure 8). Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 44 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. Figure 8 Development of crops with enhanced resilience to abiotic and biotic stress. Crops are exposed to a variety of stresses. Abiotic stresses will intensify as the following climate conditions change: water availability, precipitation, temperatures, and atmospheric CO2 levels. Biotic stres- sors that plants encounter will vary, but may consist of: bacteria, fungi, oomycetes, nematodes, viruses, and insect pests. As climate change alters environmental conditions and plant-pathogen interactions, strategies to develop more climate-ready and disease-resistant crop varieties include breeding or genome engineering approaches with stacking disease resistance genes, stacking climate tolerance and disease resistance genes, and/ or addition of beneficial microbes (see text for examples). Genome engineering tools such as CRISPR–Cas9 and tran- effects of overactive defenses. For instance, growth penalties scription activator-like effector nucleases allow greater con- associated with powdery mildew resistance in wheat were trol over the sequence and genomic location of these reversed upon ectopic activation of genes encoding sugar genetic changes. Crop engineering is an especially promising transporters through a mechanism yet to be elucidated (Li avenue for mitigating vector-borne plant diseases, which are et al., 2022). In another example, necrosis associated with anticipated to rise as higher temperatures expand the geo- broad spectrum potato virus resistance was eliminated graphical distribution and survival of insect pests (Perilla- through mutating the regulatory region of the resistance- Henao and Casteel, 2016; Huang et al., 2020; Skendzic et al., conferring immune receptor (Harris et al., 2013). 2021). For instance, introduction of proteins that target the Alternatively, protective genes can be designed to be insect vector or the pathogen itself can confer host resis- expressed under specific conditions. High temperatures in- tance. Expression of antimicrobial proteins that bind the crease susceptibility of the model plant Arabidopsis to the membrane of Xylella fastidiosa, the causative agent of bacterial pathogen Pseudomonas syringae pv. tomato Pierce’s Disease, decreased disease incidence in grapevines DC3000 (Pst; Wang et al., 2009; Huot et al., 2017). Disease re- (Vitis vinifera; Dandekar et al., 2019). Such genetic strategies sistance genes expressed under a heat-inducible promoter may lead to more effective and sustainable management of protected against Pst infection after exposure to high tem- vector-borne diseases, which have relied heavily on chemical perature without pleiotropic growth defects (Leng et al., insecticides. 2021). Another challenge is that pathogens can overcome Introduction of beneficial traits, however, have mainly fo- resistant traits by developing novel virulence strategies or by cused on the development of crop varieties with resistance evolving mechanisms to evade detection by existing im- to a single stress. Major hurdles remain in engineering crops mune receptors. Gene stacking might be used to delay or with combined stress tolerance (Steinwand and Ronald, prevent the evolution of resistance-breaking pathogens un- 2020). For one, enhanced stress tolerance is often accompa- der diverse climate stresses. nied by fitness costs, such as reduced plant growth and A promising avenue to simultaneously reduce crop loss to yields (Velásquez et al., 2018; Venkatesh and Kang, 2019). pathogen and environmental stress is introducing disease re- Additional genetic interventions can reduce detrimental sistance in the context of climate resilience (Rivero et al., Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 45 2022; Figure 8). Identification of resistance genes that are improve plant access to nutrients, particularly phosphorus more effective under abiotic stress, such as increased temper- and N. Two major groups are arbuscular mycorrhizal fungi ature, is one approach (Chen et al., 2018; Dossa et al., 2020). (AMF), which colonize host roots and are widely distributed For example, stacking the rice disease resistance genes Xa4 in plants, and ectomycorrhizae, mainly associated with trees and Xa7 provided enhanced resistance to Xanthomonas ory- and shrubs (Genre et al., 2020). The soil region influenced zae pv. oryzae (Xoo), the causal agent of bacterial blight dis- by mycorrhizal roots is called the mycorrhizosphere ease, under high temperature conditions (Dossa et al., 2020). (Priyadharsini et al., 2016), where mycorrhizal fungi sequester Alternatively, disease resistance genes can be introduced into carbon and form aggregate particles in soil that have a ma- crop varieties that already sustain high resilience to abiotic jor impact on the composition of microbial and plant com- stress. The introduction of six genes associated with resistance munities (Priyadharsini et al., 2016; Wang et al., 2021). to the fungal pathogen Magnaporthe oryzae, the causal agent Under a warmer climate, mycorrhizal fungi can increase car- of rice blast disease, into a rice variety with elevated drought bon sequestration by influencing the root/shoot ratio (Zhou tolerance resulted in plants that are both resistant to blast in- et al., 2022). Ectomycorrhizal fungi can significantly affect fection and tolerant of drought stress in the field (Carrillo the carbon sequestration capacity of certain soils, for exam- et al., 2021). Another approach is stacking genes, through ple in boreal forests (Clemmensen et al., 2015; Genre et al., breeding or genome engineering, to confer both abiotic stress 2020). Colonization by AMF can mitigate adverse effects of tolerance and disease resistance. For example, submergence drought and salt stress by improving nutrient uptake, mini- (Sub1) and salt (Saltol) tolerance genes were stacked with mizing oxidative damage, and increasing osmotic adjustment eight pathogen and pest resistance genes in an elite rice line (Hameed et al., 2014; Klinsukon et al., 2021). (Das and Rao, 2015); this line showed resistance to M. oryzae, Several challenges restrict the application of AMF in agri- Xoo and gall midge, as well as tolerance of submergence and culture as a biofertilizer. Plants vary widely in response to in- salinity. In some cases, genes can act as regulatory hubs to dividual mycorrhizal fungi (Klironomos, 2003), and results of control abiotic and biotic signaling pathways and are particu- research focusing on one or few AMF species under con- larly valuable candidates to target for crop engineering trolled conditions may not translate to field conditions. In (Husaini, 2022). For example, the rice transcription factor addition, many aspects of the signaling and nutrient ex- MADS26 orchestrates abiotic and biotic stress responses. change pathways are shared between mycorrhizal fungi and Downregulation of MADS26 led to enhanced resistance to M. biotrophic pathogens (Wang et al., 2012; Zhang et al., 2015; oryzae and Xoo as well as drought tolerance in the field Jacott et al., 2017; Jiang et al., 2017; Zhang et al., 2021a). (Khong et al., 2015). The effectiveness of each of these strate- Thus, it is critical to dissect how plants distinguish between gies to develop resilience to multiple types of stress will vary AMF- and pathogen-influenced agronomic traits and engage depending on the crop, pathogen, and environmental condi- productively with symbiotic microorganisms while simulta- tions. Research on various strategies and their evaluation un- neously restricting pathogens. der field conditions will be crucial to combat the negative Mycorrhizal fungi strongly influence host plant phospho- effects of climate change on agricultural systems. rus acquisition. Interestingly, the phosphate starvation re- sponse was found to be a core regulator in both a direct Mycorrhizal and rhizobial symbioses under climate phosphate uptake pathway via root hairs and epidermis and change challenges an indirect phosphate uptake pathway via mycorrhizal sym- (By Xiaowei Zhang, Ertao Wang) biosis (Shi et al., 2021), suggesting the possibility of develop- N cycling strongly influences climate change as it is closely ing crops that use phosphorus and N more efficiently by correlated to the production of CO2, N2O, and CH4. coordination of the direct phosphate uptake pathway and Currently, crop productivity is highly dependent on fertilizer mycorrhizal pathway in future. application, particularly N, which has negative environmen- tal effects through nitrate run-off and release of the potent N fixation in legumes and nonlegumes GHG nitrous oxide. The development of high-yielding, dis- Biological N fixation is the process by which nitrogenase (an ease-resistant crops can be aided significantly by improving enzyme found only in certain prokaryotes known as diazo- associations with symbiotic microorganisms that enhance trophs) converts dinitrogen gas from the atmosphere into nutrient assimilation in the host plant. Here, we summarize ammonia and is the main path for the formation of com- the potential application of engineered mycorrhizal and rhi- bined N in nature. Three forms of N fixation are found in zobial symbioses in developing self-fertilizing crops and nature: free-living, associative, and symbiotic (Soumare et al., maintaining sustainable agriculture in the era of global cli- 2020). In associative N fixation, N-fixing microorganisms liv- mate change (Figure 9). ing on the surfaces or in the interstitial spaces of the plant host use photosynthetic products from the plant as carbon Mycorrhizal symbiosis sources to fix N for their own use and provide the excess Plant roots are associated with diverse microbes, including fixed N to the host (Soumare et al., 2020). In symbiotic N bacteria, fungi, and viruses collectively called the rhizosphere fixation, N-fixing bacteria colonize the cells of plant organs microbiome. Among them, mycorrhizal fungi are known to such as root nodules and supply N to support host growth Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 46 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. Figure 9 Mycorrhizal symbiosis and N self-fertilizing crops. A, Positive effects of mycorrhizal symbiosis. The mycorrhizal hyphal network forms a mycorrhizosphere (light brown) which can enlarge the plant nutrient absorption area and supply a convenient zone for root-related microbes. Benefits from mycorrhizal symbiosis include increased tolerance or resistance to abiotic or biotic stresses. B, Three steps to develop N self-fertiliz- ing cereal crops to enhance climate change resilience. (1) Increasing associative N fixation. The mucilage (light green) is rich in carbohydrates and harbors abundant diazotrophic microbiota (pink). Engineered cereal plants (such as maize) have the ability to produce rhizophine, which can be perceived by engineered diazotrophs (orange). (2) Transferring symbiotic N fixation to cereal plants. Cereal crops are engineered for symbiotic N fixation by expressing the chimeric receptors perceiving rhizobia signals and overexpressing key symbiotic regulators (CSSP genes, CRE1, etc.) and nodule development genes (SCR-SHR, LBD16, etc.) to form nodule-like structures. (3) Autonomous N fixation in cereal crops. The ideal plant which could assimilate N2 into ammonium is created by overexpressing rhizobial N fixation genes in plant cells. and development, in systems such as Rhizobium/legume, Three mechanisms have been proposed to develop N self- Frankia/alder, and Cyanobacteria/Australian cycads fertilizing cereal crops to enhance climate change resilience (Pankievicz et al., 2019; Soumare et al., 2020). The rhizo- (Figure 9B): bium–legume symbiosis is the most important N fixation 1. Increasing associative N fixation. Diazotrophs are present system in terrestrial communities. in the carbon-enriched mucilage in maize aerial roots and Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 47 were found to contribute 29%–82% of the N nutrition of et al., 2013b). Transgenic Arabidopsis expressing a nine-nif Sierra Mixe maize in a 5-year field experiment (Van Deynze gene cassette (nifBHDKENXhesAnifV) showed moderate ni- et al., 2018). Engineering the cereal host and/or the diazo- trogenase activity and resulted in higher biomass and chlo- trophs to enhance this association is therefore a promising rophyll compared to control plants grown in low-N or N- avenue to increase biologically fixed N in crops. free medium (Yao et al., 2021). If the results of this study It has been shown that the engineered expression in can be validated, this will provide the possibility to construct Medicago truncatula and barley (Hordeum vulgare) of rhizo- cereal crops capable of autonomous N fixation in the future. pine, a small molecule compound synthesized by a few rhizo- bia, could be sensed by engineered bacteria Azorhizobium Enhancing climate resilience in the hardy staple caulinodans ORS571 with a 103-fold increase in perception crop cassava sensitivity (Geddes et al., 2019; Haskett et al., 2022). This pro- (By Marnin Wolfe, Eder Jorge de Oliveira, and Ismail Rabbi) vides the possibility of increasing N fixation from endophytic Cassava (Manihot esculenta) is a staple root crop grown on and free-living bacteria associated with crop plants, although more than 28 million hectares and crucial to the food secu- the in situ nitrogenase activity was suboptimal. Further experi- rity of almost half a billion people. Cassava is uniquely posi- ments should explore optimizing the expression levels of rhi- tioned as one of the most climate change resilient crops zopine biosynthetic genes to reduce fitness costs in host due to its ability to tolerate prolonged droughts, often ex- plants due to excessive gene expression. ceeding 5 months. The cultivation of cassava has continued 2. Transferring symbiotic N fixation to cereal plants. The asso- to increase in tropical regions, where climate change ciation of legumes with N-fixing bacteria requires several impacts will be particularly adverse (El-Sharkawy, 1993; Parry molecular processes common to the mycorrhizal associa- and Rosenzweig, 1993; de Oliveira Aparecido et al., 2020). In tions that are more widespread in plants, showing that the this section, we overview the innovations that have recently evolution of the Rhizobium–legume symbiosis utilized many accelerated cassava genetic improvement, the challenges existing processes that facilitate mycorrhizal interactions that drought and heat are expected to pose in coming deca- (Roy et al., 2020; Wang et al., 2022). This close relationship des, and address prospects to improve climate resilience provides a possibility to engineer symbiotic N fixation into through interdisciplinary innovations. non-legume cereal crops by synthetic biology (Mus et al., 2016). Some progress has been made toward this goal: (i) The NextGen cassava breeding project: A decade of The overexpression of chimeric receptors, for which the ex- innovation tracellular domains of the rice Myc factor receptors MYC Cassava is a clonally propagated crop domesticated in South FACTOR RECEPTOR1 (OsMYR1) and CHITIN ELICITOR America that continues to radiate throughout the tropics. RECEPTOR KINASE1 (OsCERK1) were replaced with those Phenotypic recurrent selection has been the mainstay of cas- from the M. truncatula Nod factor receptors NOD FACTOR sava breeding in much of its history. As a result of its 12- to PERCEPTION (MtNFP) and RECEPTOR-LIKE KINASE3 24-month growth cycle, low multiplication rate and low- (MtLYK3), respectively, triggers calcium spiking in response seed set, phenotypic selection requires 4–6 years between to a low concentration Nod factor treatment in rice (He crosses, a major bottleneck for genetic improvement et al., 2019). (ii) The overexpression of several symbiotic reg- (Ceballos et al., 2015). Cassava has emerged as a model for ulators induces spontaneous root-nodule-like structures the adoption of new breeding technologies among root and (Soyano et al., 2013; Tirichine et al., 2007; Yang et al., 2022). tuber crops, including the incorporation of improved experi- (iii) The key development genes in M. truncatula SHORT mental designs and phenotyping, as well marker-assisted se- ROOT (MtSHR), SCARECROW (MtSCR), and LLOB-DOMAIN lection (Mbanjo et al., 2021). PROTEIN16 (MtLBD16) specify cortical cell fate with the abil- In 2012, the Next-Generation Cassava (NGC) Breeding ity to de-differentiate to form nodule primordia in response Project initiated a multi-disciplinary effort to accelerate ge- to symbiotic signals (Schiessl et al., 2019; Soyano et al., 2019; netic improvement, notably using genomic selection at Dong et al., 2021). This constitutes a genetic toolkit to gen- breeding programs in Africa and Latin America. NGC part- erate nodule-like structures to accommodate N-fixing rhizo- ners in Africa include the International Institute of Tropical bia, that is by engineering the expression of these key Agriculture and the National Root Crops Research Institute regulators of nodule organogenesis in cereal crops. However, in Nigeria; the West Africa Center for Crop Improvement in creating the micro-aerobic conditions necessary for rhizobia Ghana; the National Crops Resources Research Institute, in the nodule organs of cereal crops to perform N fixation is still a black box. Uganda, and Makerere University in Uganda; and the Tanzania Agricultural Research Institute in Tanzania. In 3. Autonomous N fixation in cereal crops. An ideal approach South America, collaborators include EMBRAPA in Brazil for self-fertilizing cereal crops would be to make them fix N and the International Center for Tropical Agriculture in autonomously. A detailed study showed that the smallest N Colombia. In the USA, collaborators are Cornell University, fixation operon consists of 9 genes, nifB, nifH, nifD, nifK, nifE, the Boyce Thompson Institute at Cornell, the University of nifN, nifX, hesA, and nifV in Paenibacillus WLY78 (Wang Hawaii, and the USDA-ARS in Ithaca, NY. The details of Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 48 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. partners and funding found at https://www.nextgencassava. The complexity of drought-tolerance genetic architecture org. suggests that genomic selection, augmented by genome Instead of requiring phenotyping breeding lines over many editing and cutting-edge phenomics, will be necessary for years before selecting new parents, genomic selection ena- the rapid development of climate-resilient cassava varieties. bles breeders to predict performance based on genome- Currently, final yield is the basis for selection for drought tol- wide genetic markers, even at the seedling stage erance (Khadka et al., 2020). However, yield is affected by (Figure 10A). Genotyping of all germplasm and targeted many factors into drought and is only measurable after 10– phenotyping of representative subsets make breeding value 12 months. Earlier stage, nondestructive evaluation of physi- prediction in early stages possible, increasing selection inten- ological drought responses and root bulking is needed. sity and reducing selection cycle time (Heffner et al., 2009). Remote sensing of photosynthetic performance using drones The transition from phenotypic to genomic selection has with hyperspectral imaging (Verma et al., 1993; Banerjee et gained momentum in cassava through the NGC, and while al., 2020) and root yield using ground penetrating radar is breeding cycle times are 50% shorter, selection intensity and now possible (Agbona et al., 2021). High-throughput pheno- accuracy are higher (Wolfe et al., 2017), and the rate of im- typing plus genomic prediction and GWAS-based discovery provement is demonstrably increased relative to previous are powerful tools for climate-resilience breeding (Juliana decades (Figure 10B). et al., 2019; Jha et al., 2020). Pilot tests have been conducted Several additional innovations came to cassava under on cassava for association with above and below-ground NGC, including: (1) GWAS enabling the cataloging and vali- traits (Selvaraj et al., 2020). dation of trait-linked single-nucleotide polymorphisms used Genome editing and metabolic engineering are promising for marker-assisted selection (Wolfe et al., 2017; Zhang et al., supplements to exploiting existing natural diversity. 2018; Rabbi et al., 2020); (2) Cassavabase.org, an open-access, Transformation of cassava to express isopentenyl transferase breeding database for efficient management of phenotype resulted in increased water retention and leaf retention un- and genotype data (Morales et al., 2022); and (3) use of der water stress (Zhang et al., 2010). The overexpression of plant growth regulators for improved flowering and seed set transcription factors like DEHYDRATION-RESPONSIVE (Hyde et al., 2020). Genomic resources developed during the ELEMENT BINDING PROTEIN (DREB), ABA-RESPONSIVE last decade, including reference genomes (Lyons et al., 2021) ELEMENT BINDING PROTEIN1 (AREB1), and ABA- and HapMap (Ramu et al., 2017; Kuon et al., 2019) have laid RESPONSIVE ELEMENT BINDING FACTOR2 (ABF2) were a foundation for trait-discovery research. These technologies also shown to increase drought tolerance in some species collectively will enable breeders worldwide to tackle the (Rivero et al., 2007). In Arabidopsis, CRISPR/Cas9 was used food-security challenges posed by climate change. to modify the OPEN STOMATA2 (OST2) gene resulting in greater drought tolerance through enhanced stomatal re- Climate resilient cassava breeding: Innovations for the sponse (Osakabe et al., 2016). Engineering multiple traits next decade such as improving light reaction efficiency, reducing photo- Although cassava is considered a drought-tolerant species respiration, improving sucrose synthesis to increase sucrose (Okogbenin et al., 2013), there is still a large gap between loading and stimulate cambium activity could improve the yield obtained by farmers in semi-arid regions (9.5 starch synthesis and metabolite transport into storage roots t.ha–1) and yield observed under experimental water deficit and increase sink capacity (Obata et al., 2020; Sonnewald (23.6 t.ha–1) with improved genotypes (de Oliveira et al., et al., 2020). In cassava, there are no published studies on 2015). Fortunately, there is enormous genetic variability to the use of genome editing to mitigate drought response, tap for drought tolerance for future genetic improvement but several studies have demonstrated the feasibility of using (de Oliveira et al., 2017; Figure 10C). Most cassava field test- CRISPR/Cas9 for virus resistance (Gomez et al., 2019) and re- ing by breeders is done in both high-rainfall and drought- ducing cyanogenic compounds (Gomez et al., 2021). prone environments. Over the annual cropping cycle, geno- Climate change will disproportionately impact already types are routinely exposed to 3–5 months of drought and food insecure regions of the world (Easterling and Apps, higher temperatures during which they are evaluated for 2005). Cassava, already a hardy crop, can help to attenuate leaf retention, greenness, and damage by dry season pests some of those negative impacts. For example, cassava such as green mites (Ezenwaka et al., 2018). Advanced test- planted under free-air CO2 enrichment has been shown to ing is usually done in multienvironment trials, including low positively respond with increased yield and higher WUE rainfall, heat-stressed environments (Hershey, 1984). (Rosenthal et al., 2012; Ruiz-Vera et al., 2020). Given suffi- Although genetic control of drought tolerance in cassava, as cient investment, the role of cassava as a food-security and measured by yield under drought, is complex with strong industrial crop will continue to expand and serve as a buffer genotype-by-environment interaction (de Oliveira et al., to future climate change-related food insecurity. We have 2015), a recent GWAS identified candidate genes with described ways in which cassava is a “climate-smart” known association to drought tolerance and markers useful crop and an important staple for millions in the tropics. for breeding (dos Santos Silva et al., 2021). Now is the time to continue the modernization in cassava Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 49 Figure 10 Genomic selection (GS) in a cassava breeding program. A, Each breeding cycle begins with a crossing block trial where seeds are gener- ated. The first evaluation, a seedling nursery (SDN) usually involves 410K plants, but cassava does not produce storage roots when planted from seed and no yield data is collected. After 12 months, seedlings are cloned (5–10 cuttings/plant) into their first single-row, unreplicated clonal eval- uation trial (CET) followed by at least three stages of yield trials (preliminary [PYT], advanced [AYT], and uniform [UYT]). All lines entering CET are genotyped genome-wide; sometimes this is done during the seedling nursery. As a result, genomic prediction enables selection of new parents for crossing even as early as the SDN (dashed red arrow). B, GS has resulted in demonstrable acceleration in the rate of genetic improvement since initiation in 2012. Results shown are from the IITA GS population. The genomically predicted performance of GS-era (purple) and historical (yel- low) clones relative to a multi-trait selection index (y-axis) is plotted against the year when each clone was first generated (x-axis). C, Field trial showing variability for one of the major future challenges to cassava: drought. The top image shows plants 3 months after planting, under irriga- tion at Petrolina (Pernambuco, Brazil). The bottom image shows plants 3 months later under water deficit. breeding and biotechnology to benefit the most vulnerable 2019), showed similar decreases in mineral nutrients. A populations. more comprehensive set of FACE experiments were reported across three countries, with multiple sites and The carbon nutrient penalty: Will it matter? crops (Myers et al., 2014, Dietterich et al., 2015), which con- (By Gabriel Castrillo, Martin R. Broadley, and David E. Salt) firmed decreases in Zn and Fe concentration of 5%–10% for Hidden hunger, the lack of sufficient dietary micronutrients C3 grains and legumes at the elevated CO2 concentrations including iron (Fe) and zinc (Zn), is a major problem for a predicted for 2050 (546–586 ppm). A large meta-analysis significant portion of the world’s human population representing numerous FACE and non-FACE experiments (Kumssa et al., 2015; Lenaerts and Demont, 2021). also identified similar reductions in Zn, and in other dietary Experiments with plants cultivated in growth chambers mineral nutrients such as calcium (Ca) and magnesium (Mg; have suggested that elevated atmospheric CO2 is associated Loladze, 2014). This carbon nutrient penalty was projected to with a decline in mineral nutrients in a number of crops, for cause a decrease in the global availability of dietary Fe and example, decreased Fe and Zn concentrations in wheat, bar- Zn of between 2.5% and 3.6% by 2050 (Beach et al., 2019); ley, and rice (Manderscheid et al., 1995; Fangmeier et al., producing the forecast that many countries that currently 1997; Seneweera and Conroy, 1997; la Puente de et al., 2000; have high levels of hidden hunger will continue to do so. Pleijel et al., 2000). Free-air CO2 enrichment (FACE) experi- A better understanding of the impact of elevated CO2 on ments with plants grown under standard field management mineral nutrient concentrations in crops requires concomi- practices, with various crops including soybean, sorghum tant consideration of elevated temperature, as they go hand (Sorghum bicolor), potatoes, wheat, barley, and rice (Prior in hand. Combined FACE and temperature (T-FACE) experi- et al., 2008; Högy and Fangmeier, 2009; Högy et al., 2009; ments have begun to address the possible impact of ele- Erbs et al., 2010; Fernando et al., 2014a, 2014b; Ujiie et al., vated temperatures on the carbon nutrient penalty. In Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 50 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. soybean, elevated CO2 caused a decrease in seed Fe and Zn et al., 2019), and wheat (Gardiner et al., 2018). The applica- concentrations (as previously observed), while elevated tem- tion of genome-wide association mapping to this variation perature had the opposite effect; but the combined effect of has led to the identification of genes controlling variation in elevated temperature and CO2 restored seed Fe and Zn con- numerous elements (Baxter et al., 2010; Chao et al., 2012, centrations (Köhler et al., 2019). A similar compensating ef- 2014; Forsberg et al., 2015; Yang et al., 2018). Ecological stud- fect of elevated temperature on the carbon nutrient penalty ies are starting to reveal the adaptive benefit of this variation was also observed in rice and wheat (Guo et al., 2022). for coastal populations (Busoms et al., 2018, 2021). Under uniform global temperature increases, the carbon nu- Soil microbiota contributes to the biogeochemical cycling trient penalty may therefore be expected to disappear. of elements, soil regeneration, and plant and animal growth However, rising global temperatures will not be uniform and productivity (Custódio et al., 2022). In experiments with across the globe, with different regions experiencing different Arabidopsis, the root microbiome was shown to control dif- levels of warming. Predicting if elevated temperatures will ferentiation of the endodermis, a diffusion barrier that balance nutrient loss due to elevated CO2 may be more affects mineral nutrient homeostasis, through the repression complex and uncertain. of responses to the phytohormone abscisic acid in the root Improved access to diverse diets, comprising more (Salas-González et al., 2021). However, these mechanisms nutrient-dense foods, can play a role in alleviating hidden have not been evaluated under future elevated CO2 scenar- hunger. However, access to micronutrient-adequate diets is ios. Elevated CO2 in the short term increases metabolic ac- unlikely for many people in the coming decades, for socio- tivity and microbial biomass in the soil, with a concomitant economic reasons (Nelson et al., 2018). Geographical con- promotion of plant growth and root exudation, conditions straints to micronutrient availability in many food systems, that reduce soil N content (Chen et al., 2014; Xiong et al., reported from recent GeoNutrition surveys, further com- 2015; Yu et al., 2018a). Thus, in the long-term, elevated CO2 pound this challenge (Gashu et al., 2021). Interventions to is predicted to have a negative impact on the soil carbon cy- alleviate hidden hunger include supplements, food fortifica- cle, promoting the depletion of easily decomposed carbon tion, and biofortification of staple crops through breeding and increasing the degradation of mineralized SOC with a and agronomy. Zn-biofortified wheat varieties released in net increase in atmospheric CO2 (Yang et al., 2019a). India and Pakistan (Zia et al., 2020; Govindan et al., 2022), Elevated CO2 influences microbial enzymatic activities for and Zn-biofortified hybrid maize varieties in Guatemala and phosphorus and N cycling but this effect changes depending Colombia (Maqbool and Beshir, 2019) can increase grain Zn on the ecosystem (Naylor et al., 2020). We need to under- concentration by more than the anticipated decreases due stand microbiome stability in diverse ecological contexts, to elevated CO2. The continued development of crops that considering spatial resolution, microbial connectivity, and can reliably accumulate sufficient quantities of mineral multi-kingdom composition. This will allow us to feed cur- nutrients against a backdrop of climate change is an impor- rent models with realistic experimental data to predict the tant part of this solution. The use of micronutrient fertilizers impact of climate changes on soil microbial populations and (Joy et al., 2017) and “regenerative” agricultural interventions their interactions with plants, helping us to develop (Manzeke-Kangara et al., 2021) can also play a role in reduc- microbial-based strategies to alleviate climate change ing hidden hunger. impacts on soil and food production. Our understanding of mineral nutrient homeostasis in plants is extensive, with over 176 genes identified to date Can we achieve a biomass-based (Whitt et al., 2020), but far from complete. Of these known bioeconomy? genes, over 80 are characterized as ion transporters, many of which were investigated based on their predicted function (By Maureen C. McCann and Nicholas C. Carpita) as transmembrane proteins. High-throughput elemental Gross domestic product, a measure of economic prosperity, analysis of plant material, also known as ionomics (Salt is tightly correlated with energy consumption. Fossil fuels et al., 2008), has proved to be a powerful forward genetic accounted for 80% of global energy resources in 2020. Coal screening tool that allows the discovery of genes involved in and gas can eventually be displaced by renewable energy mineral nutrient homeostasis and the study of natural ge- from wind and solar, geothermal and hydroelectric, and nu- netic variation in the system (Huang and Salt, 2016). This clear energy (U.S. Department of Energy, 2015). Oil, however, approach highlights the critical importance of the Casparian provides both liquid transportation fuels and raw materials strip in the endodermal cell wall in controlling mineral nu- for the petrochemical industry. As addressing climate change trient homeostasis (Hosmani et al., 2013; Pfister et al., 2014; becomes increasingly urgent, we now need to shift from oil Kamiya et al., 2015; Reyt et al., 2020, 2021; Alcock et al., derived from long-dead organisms to living organisms that 2021). Ionomics has also revealed a global pattern of natural can provide chemicals, fuels, and materials (Carpita and variation in the leaf and seed ionome of Arabidopsis McCann, 2020). In this section, we imagine a biomass-based, (Campos et al., 2021), and in rice (Pinson et al., 2015), barley circular bioeconomy, enabled by recombinant DNA technol- (Houston et al., 2020), soybean (Ziegler et al., 2018), common ogies, with the potential to decouple our prosperity from bean (Phaseolus vulgaris; Nazir et al., 2022), peanut (Zhang fossil fuel consumption (National Academies of Science, Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 51 Engineering, and Medicine, 2020). To succeed, this bioecon- The diversity of plant metabolism, natural and engineered, omy must be fully rooted in plant biology. also provides a foundation for engineering biology to create Natural and engineered oil-accumulating plants and economic value. Living plant cells synthesize between microalgae, such as cyanobacteria, are an important source 100,000 and 1 million kinds of molecules (Fang et al., 2019). of liquid hydrocarbons for use as fuel components. To ad- Making natural or synthetic products directly in plants can dress how plants can displace a significant proportion of oil take advantage of orders-of-magnitude greater metabolic consumption also requires use of the sugars and aromatics complexity and potential product yields than can be derived from plant cell walls (McCann and Carpita, 2015). achieved in microbial chassis organisms. Efficient production Electric and hybrid vehicles powered by renewable energy of target compounds in plants will require a systems-level sources are becoming viable long-term options for light understanding of metabolism and constraints, including ground transportation (U.S. Department of Energy, 2015). tradeoffs between carbon fluxes and cellular energy However, air, marine, and heavy-duty modes of transporta- balances. tion, which contribute one-third of US transportation GHG The structural complexity of plant cell wall components emissions, will remain dependent upon energy-dense, liquid- can provide oligomeric and polymeric substrates for materi- hydrocarbon fuels for decades because of slow fleet turn- als such as thermosets, thermoplastics, composites, cellulose over: aircraft, for example, have a service lifetime of 25–30 nanocrystals, and nanofibers. Thermoset materials include years. Advanced biofuels, fully compatible with existing epoxy, silicone, and polyurethane. Lignin- and carbohydrate- engines and transportation infrastructure, can include liquid derived monomers have been incorporated into polymers to hydrocarbons produced by chemical or enzymatic catalytic create new bio-based materials with improved performance conversion of biomass-derived sugars and aromatics (Huber characteristics compared to fossil fuel-derived thermoset et al., 2003; Wang et al., 2014). materials (Zhao and Abu-Omar, 2015; Jiang et al., 2018; Plant-based biofuels also offer the potential for the pro- Chen et al., 2019). Poplar fibers have also been directly in- duction of valuable chemical co-products. Decades of re- corporated into composites with polylactic acid as a replace- search have overcome the technological barriers to the ment for conventional carbon nanofibers that reinforce production of cellulose-derived glucose and, more recently, polymers for large-scale 3D printing applications (Zhao lignin-derived aromatics. As a result of new deconstruction et al., 2019). In contrast to thermosets, thermoplastics can be melted, and some of their monomers may be recycled. technologies that preserve aromatic ring structures (Bozell The entire pathway to polyhydroxybutyrate was engineered et al., 2011; Labbé et al., 2012; Parsell et al., 2013; Socha in cotton over 25 years ago (John and Keller, 1996), and et al., 2014), lignin is no longer a major source of biomass more recently in the bioenergy crop switchgrass (Panicum recalcitrance. Catalytic depolymerization of lignin has been virgatum) (Somleva et al., 2008). Routes for the biological achieved without decomposition of cellulose or xylan, en- synthesis of polyhydroxyurethane have been envisioned abling the concept of the “lignin-first” biorefinery, where aro- (Nohra et al., 2013). When pulped wood particles are matic fuel substrates are removed before cellulose and other treated with acids, cellulose nanocrystals, and cellulose nano- carbohydrates are processed (Ragauskas et al., 2014; fibers are recovered, derivatives of which are used for several Schutyser et al., 2015; Key and Bozell, 2016; Yang et al., kinds of synthetic materials as replacements for plastics 2019b). To produce hydrocarbon fuels, deoxygenation reac- (Moon et al., 2011; Zhu et al., 2016). tions must proceed to full chemical reduction, but for Maximizing the recovery of biomass carbon into fuels and chemical products, reactions must necessarily be highly se- co-products requires flexible design capabilities to produce lective to preserve desirable functional chemical groups. The cell wall architectures that can be easily and completely petroleum industry produces a handful of platform chemi- deconstructed for current and future conversion processes cals from oil, including ethylene, propylene, C4-olefins, ben- (McCann and Carpita, 2015). As robust cell wall architec- zene, toluene, and xylene, that are oxygenated to make tens tures are integral to plant growth and development, genetic of thousands of chemicals (Wang et al., 2014; Parsell et al., variants that are tailored with regard to biomass quality for 2015). Plants synthesize highly oxygenated polymers, and conversion processes must not be compromised for yield or the chemical moieties in these structures hold tremendous sustainability traits in field performance. Major knowledge value as useful building blocks for chemical co-products. gaps include how biosynthetic products are integrated into Pathways that employ lignin-derived aromatics as substrates composite structures, how their individual structural com- to replace commodity chemicals have been envisioned using plexities contribute to molecular- to macro-scale architec- either enzymatic or chemical catalysis (Wellisch et al., 2010; tures, and how cell wall architectures might be redesigned Zakzeski et al., 2010). Controlled fractionation of biomass for production of high-value products (Carpita and with downstream catalytic upgrading provides several value- McCann, 2020). added streams for the major biomass components: xylans to Material use is tightly coupled to energy use, GHG emis- furfural (Vinueza et al., 2015), lignin to aromatics and dicar- sions, land and water use, and waste flows. About one-third boxylic acids (Zeng et al., 2015), and cellulose to hydroxyme- of global GHG emissions comes from industrial manufactur- thylfurfural (Hewetson et al., 2016). ing. To decarbonize this economic sector will require Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 52 | THE PLANT CELL 2023: 35; 24–66 Eckardt et al. changing the means of manufacture as well as the nature of soil science. Improved communication and collaboration material inputs (Chui et al., 2020). We might imagine how across disciplines and between academia and industry can to build simplified production systems with the components also be viewed as a low-tech effort that can have a strong of plant cells or make biohybrid materials outside an intact impact. Identifying and seeking out potential collaborators organism. We might imagine designing plants to synthesize who can link the research to impactful pathways should be homopolymers, heteropolymers and composite materials, a primary goal early in the planning stages of research proj- displacing structural concrete and steel with new materials ects for maximum benefit. Socio-economic and political per- like superwood (Chen et al., 2020), or developing new-to- spectives will also be crucial in determining which nature materials with advantageous properties. approaches will be adopted and how quickly they will be Food security is a paramount concern and there are land implemented. Networking, discussion, and collaboration in use issues to consider in raising crops for nonfood versus the socio-political arena and with industry, governmental, food production. Nonfood cash crops, such as—tradition- and nongovernmental organizations may also be crucial. ally—cotton (Gossypium hirsutum), tobacco, hemp, hops (Humulus lupulus), and biofuel feedstocks, to name just a few, can be of considerable value to growers and mitigate fi- Implementation nancial risk. The diversification of food and nonfood plant Many current practices have substantial potential for miti- products within a single cropping system, or a single crop, gating CO2 emissions, including reducing food and agricul- coupled with principles of sustainability and climate change tural waste, shifting to plant-based diets, reducing resilience, could thus be an advantage toward achieving deforestation coupled with afforestation/reforestation, and both food and energy security. The decarbonization of agri- restoring coastal wetlands. Some technological solutions also culture could include the use of bioenergy crops to displace have potential in the shorter term, including direct air cap- fossil fuels as a source of hydrogen for ammonia production ture, biochar, enhanced rock weathering, and bioenergy (Gencer et al., 2020) as well as displacement of fossil fuels combined with carbon capture and storage. To date, none for harvesting and drying. of these options has been implemented globally due to cost, In the USA, an annual sustainable resource of over 1.6 bil- timeline, inefficiency, lack of scalability, or an uncertain and lion tons of lignocellulosic biomass could be considered a evolving carbon price and market. Estimates for the poten- strategic carbon reserve (U.S. Department of Energy, 2016). tial of available technologies vary widely and will depend on This quantity of biomass represents double the entire an- the ability of nations to realize effective measures (Roe et al., nual output of the US agricultural system—grains, fruits, 2019). We have explored ways that plant science can help vegetables, hay, and pasture grasses. To double or triple the to tip the balance toward enhanced climate change mitiga- capacity of the current agricultural system for a biomass- tion and crop resilience. The section on enhancing carbon based bioeconomy, additional acres must be brought into capture and sequestration in annual cropping systems production, all crops must be high-yielding, and growers speaks to our immediate needs for carbon capture on a must benefit from diversification of plant products. massive scale and the possibility that plant scientists can Conclusions achieve a meaningful impact in this arena. Some of the goals of examples discussed may require years We presented examples of some plant biology-based solu- to realize fully, such as engineering C4 photosynthesis into tions that we believe show promise toward enhancing ter- rice, symbiotic N fixation into cereals, and crops that pro- restrial carbon sequestration and engineering climate duce a variety of synthetic products. Although time is press- resilient crops. Although we addressed several disparate ing, this does not make them unworthy of attention. First, topics, a few overarching conclusions emerge. aspects of these longer-term goals may provide significant Innovation benefits in the short term, and second, the need for carbon Some of the ideas described here may seem far-fetched to capture and enhancing crop resilience and food security will today’s readers, but we believe that for our planet to remain continue in the future. The need is urgent for every plant bi- inhabitable and sustainable, many of the ideas proposed ologist to consider today how their research can contribute here—or others like them—will need to be realized, and we to addressing climate change, ensuring food security, and will need plant scientists to help achieve them. achieving a sustainable biomass-based bioeconomy. Collaboration By definition, efforts to mitigate global climate change must Acknowledgments be large scale. Plant scientists contributing meaningfully in We thank two anonymous reviewers and the editors for this arena most likely will be those who seek out effective their helpful comments. Wolfgang Busch and Joanne Chory collaboration—not only with other plant scientists but also are grateful for the work of colleagues in the Harnessing with those in other disciplines, including for example agron- Plants Initiative (HPI): Julie Law, Joe Noel, Todd Michael, and omy, bioinformatics, data science, engineering, forestry, and all other HPI team members. Downloaded from https://academic.oup.com/plcell/article/35/1/24/6759373 by International Rice Research Institute user on 04 January 2023 Climate change challenges, plant science solutions THE PLANT CELL 2023: 35; 24–66 | 53 Funding Amaducci S, Zatta A, Raffanini M, Venturi G (2008) Characterisation of hemp (Cannabis sativa L.) roots under different Collaborative research in the J.K. McKay (Colorado State growing conditions. Plant Soil 313: 227 University) and C. Topp (Donald Danforth Plant Science Anantha MS, Patel D, Quintana M, Swain P, Dwivedi JL, Torres Center) labs is funded by U.S. Department of Energy RO, Verulkar SB, Variar M, Mandal NP, Kumar A, et al. (2016) Advanced Research Projects Agency-Energy award DE- Trait combinations that improve rice yield under drought: Sahbhagi Dhan and new drought-tolerant varieties in South Asia. AR0000826 (variation in NUE and root growth responses to Crop Sci 56: 408–421 N in rice breeding lines) and by funding from Wells Fargo Arai-Sanoh Y, Takai T, Yoshinaga S, Nakano H, Kojima M, IN2 (carbon sequestration potential of hemp crops grown Sakakibara H, Kondo M, Uga Y (2014) Deep rooting conferred by for grain and fiber). The work of HPI is funded by gifts from DEEPER ROOTING 1 enhances rice yield in paddy fields. Scient the TED Audacious Program, the Bezos Earth Fund, the Hess Rep 4: 5563 Atkin OK, Tjoelker MG (2003) Thermal acclimation and the dy- Corporation, SEMPRA Energy and others. The NextGen namic response of plant respiration to temperature. Trends Plant Cassava Breeding project is funded by the UK’s Foreign, Sci 8: 343–351 Commonwealth & Development Office (FCDO) and the Bill Atkinson NJ, Urwin PE (2012) The interaction of plant biotic and and Melinda Gates Foundation (Grant INV-007637). abiotic stresses: from genes to the field. J Exp Bot 63: 3523–3543 Research on improving photosynthetic water use efficiency Audu V, Ruf T, Vogt-Kaute W, Emmerling C (2022) Changes in mi- crobial biomass and activity support ecological intensification of by the A.D.B. Leakey group is funded by the Office of marginal land through cultivation of perennial wheat in organic Biological and Environmental Research in the U.S. agriculture. Biol Agric Hortic. doi: 10.1080/01448765.2022.2040589 Department of Energy, Office of Science (DE-SC0018277 and Ayub G, Zaragoza-Castells J, Griffin KL, Atkin OK (2014) Leaf res- DE-SC0018420). The C4 Rice project is funded by a grant piration in darkness and in the light under pre-industrial, current from the Bill & Melinda Gates Foundation to the University and elevated atmospheric CO2 concentrations. Plant Sci 226: of Oxford (INV-002970). Work in the P.C. Ronald lab is 120–130 Bahuguna RN, Chaturvedi AK, Pal M, Viswanathan C, Jagadish funded by gifts from the CHAN ZUCKERBERG INITIATIVE SK, Pareek A (2022) Carbon dioxide responsiveness mitigates rice and grants from the National Science Foundation (2027795 yield loss under high night temperature. Plant Physiol 188: to P.C.R.), the United States Department of Agriculture, the 285–300 National Institutes of Health (GM122968 and GM55962 to Bahuguna RN, Solis CA, Shi W, Jagadish SVK (2017) Post-flowering P.C.R.), and the Joint BioEnergy Institute funded by the US night respiration and altered sink activity account for high night temperature-induced grain yield and quality loss in rice (Oryza sat- Department of Energy (No. DE-AC02-05CH11231 to J.C.M iva L.). Physiol Plant 159: 59–73 and P.C.R.). Baker JFT, Allen LRA Jr, Boote KNJ Pickering NB (2000) Direct Conflict of interest statement. None declared. effects of atmospheric carbon dioxide concentration on whole can- opy dark respiration of rice. 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