![Chen_2022_CO2_fertilization_map.jpg][float-right]The CO2 fertilization effect describes the enhancement of plant growth and productivity driven by elevated atmospheric carbon dioxide concentrations, primarily through accelerated photosynthesis and reduced photorespiration, resulting in increased biomass accumulation and crop yields.[1][2]Empirical evidence from free-air CO2 enrichment (FACE) experiments demonstrates average yield increases of 12-14% for major crops under elevated CO2 levels approximating future projections, with higher responses up to 35% observed in high-yield rice cultivars.[3][4]Satellite observations further corroborate this, attributing approximately 70% of the globalgreening trend since the 1980s to CO2 fertilization, alongside contributions from nitrogen deposition and land management.[5][6]This effect plays a pivotal role in the terrestrial carbon sink, with analyses estimating that CO2-driven photosynthesis enhancements have added 13.5-15.9 PgC annually to global vegetation uptake in recent decades.[7] However, its persistence faces constraints from nutrient availability, waterstress, and climate interactions, as some studies report a potential decline in marginal benefits over time due to soilnutrient limitations, though eddy covariance data and forest FACE results indicate sustained enhancements under diverse conditions.[8][9][10]Controversies arise regarding the effect's long-term magnitude, with debates over nutrient dilution potentially reducing crop nutritional quality and varying regional responses influenced by aridity or temperature, yet field-based syntheses affirm net positive impacts on C3 plant productivity absent overriding stressors.[11][12]
Definition and Mechanism
Biochemical and Physiological Processes
The CO2 fertilization effect arises primarily from enhanced photosynthetic carbon fixation, particularly in C3 plants, where elevated atmospheric CO2 increases substrate availability at the site of ribulose-1,5-bisphosphate carboxylase/oxygenase (Rubisco), the key enzyme in the Calvin-Benson cycle. This favors the carboxylation of ribulose-1,5-bisphosphate (RuBP) over its oxygenation, directly elevating the rate of CO2 assimilation into organic compounds. Free-Air CO2 Enrichment (FACE) experiments, exposing crops and natural vegetation to CO2 levels around 550-600 ppm, have demonstrated net photosynthesis increases of approximately 31% compared to ambient conditions (around 370-400 ppm during study periods).[13]A parallel biochemical process is the suppression of photorespiration, in which Rubisco's oxygenation activity initiates a cycle that releases previously fixed CO2 and consumes ATP and NADPH without net carbon gain. Under current ambient CO2, photorespiration can dissipate 20-25% of photosynthetic electron transport at 25°C, with rates rising exponentially at higher temperatures; elevated CO2 inhibits this by competitively reducing the oxygenation-to-carboxylation ratio (Vc:Vo), thereby improving carbon fixation efficiency. This effect is most pronounced in C3 species, where photorespiration represents a significant energetic cost, but negligible in C4 plants due to their inherent CO2-concentrating mechanisms that minimize oxygenation.[13][14]Physiologically, elevated CO2 triggers stomatal closure, reducing conductance by about 20% in FACE settings, which limits transpirational waterloss while maintaining adequate internal CO2 for Rubisco saturation. This adjustment enhances intrinsic water-use efficiency (WUE, defined as carbon assimilated per unit water transpired) by roughly 48%, as evidenced in long-term field data spanning the rise from pre-industrial to modern CO2 levels. However, chronic exposure induces acclimation responses, including down-regulation of Rubisco content and activity—often by 10-20% after months to years—driven by feedback from accumulated carbohydrates like sucrose and starch, which signal reduced nitrogen investment in photosynthetic machinery.[13][15]
Variations Across Plant Types
The CO2 fertilization effect varies significantly across plant photosynthetic pathways, primarily due to differences in carbon fixation mechanisms and stomatal responses. C3 plants, which comprise approximately 85% of plant species including most trees, temperate crops like wheat and rice, and many herbaceous species, exhibit the strongest relative growth enhancement from elevated CO2. In these plants, higher CO2 concentrations suppress photorespiration—a process where Rubisco oxygenase activity competes with carboxylation—and improve water-use efficiency by allowing partial stomatal closure without curtailing carbon assimilation. Meta-analyses of Free-Air CO2 Enrichment (FACE) experiments indicate that doubling atmospheric CO2 from pre-industrial levels (around 280 ppm to 560 ppm) typically boosts C3biomass by 20-40%, with yield increases averaging 19% for C3 crops at CO2 levels rising from 353 to 550 ppm.[16][17]C4 plants, such as maize, sorghum, and tropical grasses, demonstrate a muted response to CO2 enrichment because their bundle-sheath anatomy already concentrates CO2 around Rubisco, minimizing photorespiration even at ambient levels. This adaptation, evolved for hot, dry environments, results in negligible or small biomass gains (often 0-10%) under elevated CO2, as confirmed by long-term field studies and meta-analyses showing C4 yields largely unaffected by CO2 rises to 550 ppm.[17][16] Consequently, rising CO2 can shift competitive advantages toward C3 species in mixed ecosystems, potentially altering grassland compositions where C4 dominance prevails under current conditions.[18]Crassulacean acid metabolism (CAM) plants, including succulents like agaves and cacti adapted to arid habitats, display intermediate responses, with biomassproductivity increasing by an average of 35% under doubled CO2 concentrations. CAM species fix CO2 nocturnally via phosphoenolpyruvate carboxylase, storing it as malic acid for daytime decarboxylation and Rubisco activity, which reduces water loss but limits overall photosynthetic rates compared to C3 or C4. Elevated CO2 enhances this efficiency by boosting nocturnal uptake and reducing daytime stomatal opening, though benefits may plateau if nutrient limitations arise; experimental data from species like Agave vilmoriniana confirm positive growth effects without the pronounced photorespiration relief seen in C3 plants.[19] These pathway-specific variations underscore that while global greening trends are dominated by C3-dominated forests and crops, C4 and CAM biomes may experience subdued or context-dependent fertilization, influenced further by local factors like soil nutrients and temperature.[20]
Historical Context and Early Evidence
Discovery and Initial Observations
The essential role of atmospheric carbon dioxide (CO₂) in plant growth was established in the early 19th century through experiments demonstrating its fixation during photosynthesis. In 1804, Nicolas-Théodore de Saussure conducted precise measurements showing that CO₂ serves as the primary carbon source for plant biomass accumulation, with growing plants incorporating carbon from the atmosphere into organic matter while releasing oxygen.[21] These findings built on earlier work by Jean Senebier, who in the late 18th century confirmed that plants require CO₂ for "fixed air" assimilation in the presence of light, but de Saussure quantified the mass balance, revealing that plant dry weight gains exceed absorbed CO₂ mass due to water integration.[22]By the late 19th century, researchers began observing that ambient CO₂ levels could limit growth rates, marking the initial recognition of a potential fertilization effect. In 1879, Thomas Ball noted plants' sensitivity to atmospheric CO₂ variations, countering prevailing views that dismissed such dependency.[23] Wilhelm Pfeffer advanced this understanding through pioneering controlled experiments in growth chambers, the first such setups for seed plants, where he depleted CO₂ in enclosed environments and observed stunted vegetative development. Supplementing with elevated CO₂ restored and accelerated growth, establishing CO₂ as a limiting factor for photosynthesis and biomass production. Pfeffer detailed these results in his 1897 Pflanzenphysiologie textbook, providing empirical evidence that higher CO₂ concentrations enhance plant productivity under non-limiting light and nutrients.[24]These laboratory demonstrations laid the groundwork for recognizing the CO₂ fertilization effect, though initial observations were confined to short-term chamber studies on individual plants or small groups. Pfeffer's work highlighted causal mechanisms via osmotic and physiological responses, showing dose-dependent growth enhancements without invoking unverified assumptions about long-term acclimation. Early 20th-century horticultural applications in greenhouses further corroborated these findings, with practitioners noting improved yields from CO₂ enrichment, though systematic field validations emerged later.[25]
Pre-Satellite Era Studies
Early investigations into the CO2 fertilization effect prior to the widespread use of satellite remote sensing relied on controlled enclosure experiments, primarily in greenhouses and phytotrons, to quantify plant responses to elevated atmospheric CO2 concentrations. These studies, dating back to the late 19th century, demonstrated that increasing CO2 beyond ambient levels enhanced photosynthesis and biomass production in various plant species by alleviating the limitation imposed by CO2 availability in the Calvin cycle. Wilhelm Pfeffer's foundational work in the 1890s, using early growth chambers, provided the first experimental evidence that CO2 acts as a limiting factor for vegetative growth, with plants exhibiting accelerated development when supplied with higher CO2 levels in enclosed setups.[26][27]In the mid-20th century, quantitative greenhouse experiments on crops such as wheat, rice, and soybeans consistently reported biomass increases of 20-50% under CO2 doublings from pre-industrial levels (around 280-300 ppm to 560-600 ppm), with greater responses observed in C3 plants due to improved carboxylation efficiency and reduced photorespiration. For instance, studies in the 1940s and 1950s by researchers like Gaastra measured elevated net assimilation rates in leaves exposed to 400-1000 ppm CO2, attributing gains to higher intercellular CO2 partial pressures that minimized Rubisco's oxygenase activity. These findings were corroborated in phytotron facilities established post-World War II, where controlled conditions allowed isolation of CO2 effects from confounding variables, though results varied with nutrient availability and light intensity—nutrient-limited plants showed diminished responses.[28][29]Field-scale approximations emerged in the 1960s and 1970s through open-top chambers (OTCs), which minimized enclosure artifacts compared to fully closed greenhouses; early OTC trials on soybeans in 1975 reported yield enhancements of up to 40% at 550 ppm CO2, alongside improved water-use efficiency from partial stomatal closure. However, these pre-satellite studies were constrained by small plot sizes (often <1 m²), potential microclimate alterations, and focus on single-season crops, limiting extrapolation to natural ecosystems or long-term dynamics. Meta-analyses of over 100 such experiments conducted before 1980, synthesizing data from diverse setups, estimated an average 33% increase in plant dry weight per 300 ppm CO2 enrichment, establishing the effect's robustness while highlighting dependencies on environmental co-factors like temperature and soil fertility.[29][30]
Observational Evidence from Global Monitoring
Satellite-Derived Greening Trends
Satellite remote sensing data, primarily from instruments such as the Advanced Very High Resolution Radiometer (AVHRR) and Moderate Resolution Imaging Spectroradiometer (MODIS), have revealed a widespread greening trend in global vegetation since the early 1980s, measured through increases in the Normalized Difference Vegetation Index (NDVI) and Leaf Area Index (LAI). From 1982 to 2015, growing season integrated LAI increased persistently over 25% to 50% of the global vegetated land area, equivalent to an addition of green leaf area exceeding twice the continental United States.[31] This greening is evident across diverse biomes, including forests, croplands, and grasslands, with particularly strong signals in China and India due to both environmental and land-use factors.[31]Attribution analyses using ecosystem models indicate that elevated atmospheric CO2 concentrations are the dominant driver of this observed greening, accounting for approximately 70% of the trend, while nitrogen deposition and climate factors contribute smaller shares of 9% and 8%, respectively.[31] Land-use management explains the remainder but is secondary when isolated in simulations. These findings align with biophysical principles where higher CO2 enhances photosynthesis and reduces water loss through stomatal closure, promoting leaf expansion particularly in water-limited regions.[5] Recent extensions of the record through 2020 confirm the persistence of greening, with 55% of global land areas showing accelerated rates from 2001 to 2020, concentrated in regions like India and boreal zones.[32]However, some analyses detect a slowdown or regional browning amid ongoing greening, potentially linked to nutrient limitations diminishing the CO2 fertilization effect (CFE) over time. Global CFE declined from 1982 to 2015, correlating with soilnutrient availability, suggesting saturation in responsive ecosystems.[8] Despite this, 2020 marked the record highest vegetation greenness in satellite records since 2000, attributed partly to CO2 alongside favorable weather in temperate and boreal areas.[33] Model simulations controlling for land use reinforce CO2's primacy, attributing nearly all residual greening to fertilization rather than climate alone.[34] These trends underscore CO2's causal role while highlighting interacting constraints like aridity and nutrients that modulate long-term responses.[35]
Eddy Covariance and Flux Tower Data
Eddy covariance flux towers measure turbulent fluxes of CO2, water vapor, and energy at ecosystem scales using high-frequency sensors on towers, providing direct estimates of gross primary productivity (GPP) and net ecosystem CO2 exchange (NEE) without relying on models or enclosures.[36] Networks like FLUXNET, comprising over 1,000 sites worldwide since the 1990s, aggregate these observations to detect long-term trends in carbon uptake attributable to rising atmospheric CO2 concentrations.[37]Analyses of FLUXNET data have isolated the CO2 fertilization effect (CFE) by partitioning GPP trends against climatic variables, revealing enhanced photosynthetic rates concurrent with CO2 increases of approximately 50 ppm since the 1980s.[37] A 2022 global assessment of eddy covariance records estimated CFE as a 5.3 ± 2.5% increase in GPP per 100 ppm CO2 rise, with stronger effects in water-limited ecosystems due to concurrent improvements in water-use efficiency.[37] This quantification aligns with biochemical expectations of Rubisco saturation under elevated CO2, as flux data show reduced midday photosynthetic depression and elevated seasonal carbon assimilation.[36]In extratropical forests, a 2023 statistical decomposition of 38 long-term flux tower records (spanning 1990–2020) attributed a productivity gain of 3.2 ± 0.9 gC m⁻² yr⁻¹ per ppm CO2 increase to sustained photosynthetic stimulation, independent of temperature or precipitation trends.[38] These sites, primarily deciduous and coniferous stands, exhibited persistent CFE without evidence of saturation over decades, supporting causal inference from CO2's role in carboxylation kinetics.[39]Flux data further indicate that CFE contributes 20–50% to observed multidecadal GPP enhancements in temperate and boreal biomes, with residual variability linked to nitrogen availability or disturbance.[40]However, some flux tower syntheses report a weakening CFE in recent years, with a global decline in the sensitivity of GPP to CO2 inferred from FLUXNET trends post-2000, potentially due to nutrient constraints or vapor pressure deficit stress overriding fertilization benefits.[8] Despite this, baseline evidence from eddy covariance confirms CFE as a dominant driver of historical carbon sink strengthening, with site-level anomalies in NEE aligning more closely with CO2 anomalies than alternative forcings in controlled attribution studies.[41]
Experimental Validation
Controlled Chamber Experiments
Controlled chamber experiments, typically conducted in sealed growth chambers, greenhouses with CO2 enclosures, or phytotrons, enable precise manipulation of atmospheric CO2 concentrations while controlling variables such as temperature, light, humidity, and nutrients to isolate the direct physiological impacts of elevated CO2 on plants. These setups minimize external influences like wind or pests, providing baseline evidence for the CO2 fertilization effect primarily through enhanced carboxylation in the Calvin-Benson cycle and suppression of photorespiration in C3 plants.[15][42]In C3 species, which include major crops like wheat, rice, and soybeans as well as most trees and forbs, elevated CO2 (often 550-700 ppm, roughly double ambient levels) consistently boosts light-saturated net photosynthesis by 30-50%, depending on species and conditions, due to increased Rubisco efficiency and reduced oxygenase activity.[15][14] This photosynthetic enhancement translates to biomass increases averaging 25-35% across meta-analyses of chamber studies, with above-ground dry matter rising more than roots in nutrient-replete conditions, though root:shoot ratios can shift under nutrient limitation.[43][44] For woody plants, chamber experiments report similar gains, with photosynthetic rates up 40% and total biomass up 20-30% at doubled CO2, alongside improved water-use efficiency via partial stomatal closure reducing transpiration by 20-40% without proportionally curtailing CO2 uptake.[45][42]Crop-specific responses in chambers highlight yield potentials: rice shows 15-25% grain yield increases at 550 ppm, wheat 20-30%, and soybeans 10-20%, often with faster development and higher harvest indices under non-stressed conditions.[46][15] C4 plants, such as maize and sorghum, exhibit smaller benefits (5-15% biomass gain), mainly under water or light stress where CO2 concentrates at the bundle sheath enhances efficiency.[47] However, chamber results can be moderated by interactions; for instance, nitrogen limitation reduces the fertilization effect by 50% or more, as excess carbohydrates dilute tissue N concentrations by 10-15%.[43] Elevated CO2 also alters morphology, increasing leaf area index by 10-20% initially but potentially leading to earlier senescence if sinks are saturated.[14]While chambers provide causal evidence for CO2-driven growth enhancements under idealized conditions, methodological artifacts—such as constant CO2 exposure without diurnal fluctuations, elevated humidity, or restricted airflow—may inflate responses compared to open-field validations, with meta-analyses indicating 10-20% higher biomass gains in chambers versus free-air systems.[47][48] Nonetheless, these experiments underpin the biochemical mechanisms, confirming that CO2 acts as a primary limiter to C3 productivity in current atmospheres.[15]
Free-Air CO2 Enrichment (FACE) Studies
Free-air CO2 enrichment (FACE) experiments expose crops, forests, and natural ecosystems to elevated atmospheric CO2 concentrations in open-field conditions, using blowers and tubing to release CO2 without the artifacts of enclosed chambers, such as altered light, humidity, or wind.[47] These studies, initiated in the early 1990s, typically target CO2 levels of 475–600 ppm, simulating future projections, and span multiple growing seasons to assess long-term responses.[47] Unlike chamber experiments, FACE minimizes edge effects and maintains natural environmental variability, providing more realistic data on CO2 fertilization.[49]Major FACE facilities include the Duke Forest experiment (1996–2005) on loblolly pine in North Carolina, which demonstrated sustained increases in net primary production (NPP) and biomass accumulation under elevated CO2, with carbon sequestration enhanced by 20–30% over a decade, though limited by nutrient availability.[49] SoyFACE in Illinois (2001–present) examined soybeans, revealing yield increases of 10–15% from elevated CO2, driven by greater pod set and seed mass, but moderated by interactions with ozone exposure.[50] RiceFACE and wheat FACE trials in Asia and Australia reported grain yield gains of 8–12% for rice and similar for wheat under +200 ppm CO2, with higher-yielding cultivars showing up to 35% enhancement due to improved tillering and grain filling.Meta-analyses of FACE data across 186 studies of C3 crops indicate an average 18% yield increase under non-stress conditions with ~200 ppm CO2 elevation, attributed to enhanced photosynthesis and reduced photorespiration, though responses diminish under drought or high temperatures, where yield offsets can reach 10–35%.[51] Forest FACE experiments, such as those at Duke, confirmed greater responsiveness in woody plants, with 20–40% boosts in above-ground biomass, but progressive nutrient dilution and soil constraints limited sustained gains beyond initial years.[47] Overall, FACE evidence supports CO2-driven improvements in water-use efficiency by 20–50% via partial stomatal closure, yet highlights interactions with nitrogen limitation and pests that cap net benefits in real-world settings.[47] These findings underscore FACE's role in validating observational greening trends while revealing context-dependent limitations not captured in models assuming uniform fertilization.[52]
Key FACE Findings on Crops and Forests
FACE experiments on crops, conducted at sites such as SoyFACE in Illinois and rice paddies in Japan, have demonstrated that elevating atmospheric CO2 to approximately 550 ppm typically increases yields of C3 crops by an average of 18% under non-stress conditions, based on a meta-analysis of 186 studies across 18 crop species.[51] This enhancement arises primarily from improved photosynthetic efficiency and reduced photorespiration in C3 plants, with greater responses observed in legumes (up to 25-30% yield gains) compared to cereals like wheat and rice (10-15%).[47] However, C4 crops such as maize exhibit smaller or negligible yield increases (around 0-8%), due to their inherent CO2 concentrating mechanisms that minimize photorespiration even at ambient levels.[53]In forest ecosystems, FACE studies like the Duke Forest experiment with loblolly pine (Pinus taeda) revealed sustained increases in net primary productivity (NPP) of about 20-25% under elevated CO2 (to 565 ppm), translating to a 27% greater annual biomass increment (108 g C m⁻² year⁻¹) compared to controls over multiple years.[54] Similarly, the Oak Ridge National Laboratory FACE site with sweetgum (Liquidambar styraciflua) showed comparable NPP enhancements of 21.8% when normalized to a 41% CO2 increase, with benefits persisting through nutrient limitations via improved carbon allocation to roots and fine litter production.[10] These findings indicate that mature forests respond positively to CO2 fertilization through elevated photosynthesis and belowground carbon investment, though long-term gains may be constrained by nitrogen availability, as evidenced by reduced effects in N-limited stands.[55]Across both crops and forests, FACE results underscore acclimation challenges: initial photosynthetic stimulation often diminishes over time due to source-sink imbalances or nutrient feedbacks, yet overall biomass and yield accrual remains positive without overriding limitations.[56] Elevated CO2 also consistently improves water-use efficiency by 20-50% in both systems, mitigating drought stress but not fully offsetting high-temperature reductions in crop yields.[57] These open-air validations confirm chamber-based predictions while highlighting interactive effects with edaphic factors.
Impacts on Agriculture and Ecosystems
Enhancements in Crop Yields and Biomass
Free-Air CO2 Enrichment (FACE) experiments, conducted since the 1990s, provide direct evidence of yield enhancements in major crops exposed to atmospheric CO2 concentrations elevated by 200-550 ppm above ambient levels. These open-field studies, which minimize enclosure artifacts, have shown average yield increases of 12-20% for C3 crops such as wheat, rice, and soybeans under non-limiting water and nutrient conditions. For rice specifically, FACE trials reported an average 14% yield gain, with elite high-yield cultivars achieving up to 35% increases due to improved photosynthetic efficiency and resource allocation to reproductive structures.[3][51]Wheat and soybean yields in FACE setups similarly exhibit 10-15% enhancements, attributed to extended photosynthetic durations and reduced photorespiration in C3 pathways, though C4 crops like corn show smaller responses of around 5-10% owing to their inherent CO2-concentrating mechanisms. Observational analyses of US field data from 1983-2020 further corroborate these effects, estimating that each 1 ppm rise in atmospheric CO2 has driven yield boosts of 1% for wheat, 0.6% for soybeans, and 0.4% for corn, accounting for a substantial portion of historical productivity gains beyond agronomic improvements.[4]Biomass production across crops also rises under elevated CO2, with meta-analyses of enclosure and FACE studies indicating 10-15% increases in aboveground biomass, driven by greater leaf area index and carbon assimilation rates. Vegetable crops demonstrate comparable gains; for example, elevated CO2 at 800-900 μmol mol⁻¹ boosted yields of lettuce by 18%, carrots by 19%, and parsley by 17% through accelerated vegetative growth and biomass accumulation. These enhancements stem from the fundamental biochemical response where higher CO2 substrate availability elevates carboxylation rates in Rubisco, the primary photosynthetic enzyme, leading to net carbon gains that manifest as expanded root, stem, and harvestable biomass.[59][60]
Improvements in Water Use Efficiency
Elevated atmospheric CO₂ concentrations improve plant water use efficiency (WUE), defined as the ratio of carbon assimilation to water loss via transpiration, through reduced stomatal conductance that conserves water while maintaining photosynthetic productivity. This physiological response allows plants to fix more carbon per unit of water transpired, with meta-analyses of woody plants showing average stomatal reductions of 32% and WUE increases of 34% to 63% depending on CO₂ elevation levels above ambient.[44] In C₃ plants, which dominate global vegetation, this effect stems from enhanced carboxylation efficiency and suppressed photorespiration under higher CO₂, enabling partial stomatal closure without yield penalties.[61]Free-air CO₂ enrichment (FACE) experiments provide field-level validation, demonstrating intrinsic WUE gains of 73% in sweetgum (Liquidambar styraciflua) and 77% in loblolly pine (Pinus taeda) across multiple sites under approximately 550 ppm CO₂.[62] Similarly, in crop systems, FACE trials with potatoes reported WUE enhancements of 70% in one season and over 100% in another, attributed to sustained biomass accumulation amid reduced evapotranspiration.[63] For grain legumes like peas, elevated CO₂ slowed soil water depletion by boosting WUE, preserving nodule function and extending growth under limited irrigation.[64] These findings align with eddy covariance observations, where ecosystem WUE rises are driven more by CO₂-induced fertilization than isolated stomatal effects, though spatial variations occur due to vegetation type and climate.[65]Under drought conditions, elevated CO₂ further amplifies WUE benefits by alleviating water stress; for instance, it improved leaf water status in grasslands without conserving soil moisture overall, but by optimizing transpiration efficiency.[66] Crop-specific meta-analyses confirm gains of 28% in maize and up to 50% in wheat, enabling yield stability despite nutrient or water constraints.[11] Globally, rising CO₂ has contributed to observed WUE increases in vegetation, partially offsetting warming-induced evapotranspiration demands, as evidenced by flux tower data and modeling calibrated against FACE results.[67] However, these improvements are modulated by interactions with vapor pressure deficit and soil moisture, with recent studies noting potential plateaus in some biomes due to concurrent nutrient limitations.[8]
Effects on Ecosystem Productivity
Elevated atmospheric CO2 concentrations stimulate photosynthesis in C3 plants, which dominate terrestrial ecosystems, leading to increased gross primary productivity (GPP) and net primary productivity (NPP).[7] This CO2 fertilization effect has contributed to a 13.5 ± 3.5% rise in global annual terrestrial photosynthesis from 1981 to 2020, equivalent to an additional 15.9 ± 2.9 PgC sequestered.[7] Observational data from satellites further corroborate this, showing widespread "global greening" where leaf area index has increased by approximately 5-10% over recent decades, with CO2 fertilization accounting for about 70% of the effect.[5]Free-air CO2 enrichment (FACE) experiments in natural ecosystems, such as forests and grasslands, demonstrate productivity enhancements typically ranging from 10-25%. For instance, meta-analyses of forest FACE sites report a 21.8% increase in NPP under CO2 enrichment normalized to +41 ppm.[10] These gains are particularly pronounced in water-limited ecosystems, where CO2-induced improvements in water-use efficiency amplify biomass accumulation during favorable conditions.[68] In drylands, which cover about 40% of Earth's land surface, CO2 fertilization has driven vegetation expansion and higher productivity despite rising aridity.[69]Ecosystem-level responses include shifts in community composition favoring productive species and greater carbon allocation to roots, enhancing soil carbon storage in some cases.[70] Long-term monitoring at sites like Duke FACE has observed sustained woody biomass increases of 20-30% over a decade under elevated CO2, indicating potential for enduring productivity boosts absent nutrient limitations.[71] However, the magnitude of these effects varies by biome, with tropical forests showing smaller relative gains compared to temperate regions due to baseline high productivity.[72]
Nutritional and Compositional Changes
Alterations in Crop Nutrient Density
Elevated atmospheric CO2 concentrations reduce the concentrations of essential nutrients in many C3 crops through mechanisms including carbohydrate dilution, where enhanced photosynthesis increases biomass but nutrient uptake lags, and decreased transpiration limiting mass-flow delivery of soil minerals to roots.[73] Free-air CO2 enrichment (FACE) studies across wheat, rice, maize, soybeans, and other staples consistently show declines in protein, zinc, iron, and other micronutrients by 5-15% under CO2 levels of 546-586 ppm, with meta-analyses confirming average reductions of 5.9% in protein, 9.6% in zinc, and 8.0% in iron for edible portions.[74][73] These effects stem from altered carbon-nitrogen balances and suppressed expression of nutrient transporters, as observed in controlled and field experiments.[75]While macronutrients like phosphorus and potassium show variable responses, with some FACE trials reporting increases averaging 23.5% in sulfur, phosphorus, potassium, and magnesium under specific conditions, micronutrient declines predominate for human health-relevant elements, exacerbating risks of deficiencies when diets rely on these crops.[76] Reduced B vitamins and antioxidants further compound the nutritional downgrading, independent of yield gains, as nutrient density per caloric unit falls.[77] Genetic variation exists, with certain crop germplasm exhibiting resilience to maintain concentrations, suggesting potential for breeding countermeasures.[3]Projections indicate that by 2050, under rising CO2 without interventions, global dietary intakes of zinc and iron from crops could decrease by 3.1-9.7% and 3.8-5.1%, respectively, heightening "hidden hunger" in populations dependent on staples like rice and wheat.[74] Interactions with soil fertility and management practices modulate these alterations, but empirical data from multi-year FACE sites underscore the pervasive dilution trend absent enhanced fertilization.[78]
Implications for Food Quality and Human Nutrition
Elevated atmospheric CO2 concentrations reduce the nutritional quality of many staple crops by decreasing the concentrations of essential macronutrients and micronutrients, despite increases in overall biomass and yield. This phenomenon, observed in free-air CO2 enrichment (FACE) experiments and meta-analyses, primarily affects C3 plants such as wheat, rice, and soybeans, where protein content declines by 5-15% under CO2 levels projected for mid-century (e.g., 550 ppm).[79][80] For instance, wheat grains exhibit 6-8% lower protein, while rice shows reductions in zinc by up to 9.3% and iron by 5.1%.[79][81]These changes stem from the dilution effect, where enhanced photosynthesis boosts carbohydrate production more than nutrient uptake, alongside reduced transpiration that limits mineral absorption from soil. Minerals like zinc, iron, and magnesium decrease consistently across studies, with meta-analyses confirming average declines of 5-10% in edible portions of grains and legumes.[82][73] Some vitamins, such as B vitamins in rice, also diminish by 10-30%, exacerbating the issue.[81] In vegetables, effects vary, but staples critical to global diets show net losses in nutrient density.[60]For human nutrition, these alterations pose risks of widespread deficiencies, particularly in regions dependent on plant-based diets lacking diverse animal proteins or supplements. Projections indicate that by 2050, under elevated CO2, dietary supplies of zinc and iron could fall by 3-17% in high-rice-consuming countries like Bangladesh and Vietnam, potentially affecting over 150 million people with protein-energy malnutrition or micronutrient shortfalls.[81][83] Increased caloric yields may mask the problem in yield-focused agriculture, leading to "hidden hunger" where populations consume sufficient calories but inadequate nutrients, contributing to anemia, stunted growth, and weakened immunity.[77] Empirical data from FACE sites underscore that without interventions like enhanced fertilization or crop breeding for nutrient retention, these nutritional declines could offset gains in food quantity.[73][80]
Limiting Factors and Interactions
Nutrient and Soil Constraints
The CO2 fertilization effect on plant growth is frequently constrained by the availability of essential soilnutrients, particularly nitrogen (N) and phosphorus (P), which limit the capacity for increased biomass production and photosynthesis under elevated CO2 concentrations.[84] In nutrient-limited environments, initial enhancements in net primary productivity (NPP) from CO2 enrichment often diminish over time as plants deplete available resources faster than they can be replenished, a phenomenon known as progressive nutrient limitation.[85] Free-air CO2 enrichment (FACE) experiments demonstrate that without supplemental fertilization, the stimulatory impact of elevated CO2 on crop yields and forest growth is reduced by up to 50% or more in N-poor soils.[86][11]Nitrogen limitation is the predominant constraint globally, affecting approximately 65% of vegetation types and leading to dampened CO2-driven increases in gross primary productivity (GPP).[84] Long-term observations, such as the 11-year Duke FACE study in a loblolly pineforest, revealed that N scarcity progressively curtailed NPP enhancement from 24% initially to near zero by the experiment's end, as foliar N concentrations declined and soil N cycling failed to keep pace with carbon demands.[85] Similar patterns occur in crops; for instance, in wheat and rice under FACE conditions, N limitation halved expected yield gains from CO2 elevation, with plants exhibiting reduced photosynthetic capacity due to lower rubisco activity tied to N availability.[86] A global analysis of satellite data from 1982 to 2015 further indicates a recent decline in the CO2 fertilization effect on vegetation photosynthesis, attributed in part to widespread N constraints exacerbated by soil depletion and reduced foliar N trends.[8]Phosphorus limitation plays a significant role in specific ecosystems, constraining CO2 effects in about 25% of global vegetation, particularly in tropical forests and P-depleted soils.[84] Studies in tropical regions show that P scarcity weakens the CO2 fertilization impact on the carbon cycle, with elevated CO2 failing to boost growth where soil P stocks are low, as evidenced by minimal changes in aboveground biomass despite increased fine root production aimed at P foraging.[87] In agricultural contexts, P constraints under elevated CO2 lead to trivial growth enhancements across varying P application rates, underscoring the nutrient's role in limiting metabolic scaling of CO2 benefits.[88] Latitudinal gradients amplify these effects, with stronger N and P limitations in boreal and tropical soils compared to temperate zones, influencing projections for ecosystem carbon sinks.[89]Soil properties beyond bulk nutrient content, such as texture, pH, and microbial activity, further modulate these constraints through influences on nutrient cycling and plant-soil feedbacks.[90] Elevated CO2 can accelerate soil organic matter decomposition in N-limited systems, paradoxically intensifying N drawdown via enhanced microbial demand, as observed in decade-long experiments where N enrichment amplified CO2 stimulation of soil respiration but depleted available N pools.[91] In nutrient-stressed soils, rootproliferation under CO2 enrichment improves short-term nutrient uptake but often fails to sustain long-term gains without external inputs, highlighting the interplay between soil fertility and the durability of fertilization effects.[92] Overall, these nutrient and soil factors imply that the net terrestrial carbon sink from CO2 fertilization may be overstated in models neglecting site-specific limitations.[93]
Water Availability and Vapor Pressure Deficit
Elevated atmospheric CO2 concentrations enhance plant water use efficiency (WUE) by reducing stomatal conductance, which decreases transpiration while sustaining or increasing photosynthesis, thereby alleviating constraints from limited water availability.[94] In Free-Air CO2 Enrichment (FACE) experiments across various ecosystems, stomatal conductance declined by an average of 22% under CO2 levels elevated by approximately 200 ppm, leading to 20-40% improvements in intrinsic WUE (photosynthesis per unit transpiration).[94] This physiological response allows plants to maintain productivity under soil moisture deficits, as demonstrated in wheat and soybean trials where elevated CO2 increased yields by 10-15% during drought conditions despite unchanged water inputs.[95]However, interactions with vapor pressure deficit (VPD)—the driving force for transpiration—increasing due to higher temperatures can partially offset these benefits. Rising VPD, observed to have increased globally by 0.3-0.5 kPa per decade since the 1980s, amplifies evaporative demand, potentially negating CO2-induced WUE gains if VPD exceeds 2-3 kPa during heatwaves.[96] In controlled experiments with tree species, elevated CO2 mitigated VPD-driven water stress by 15-25% through coordinated stomatal closure, but under combined high VPD and drought, net WUE improvements diminished to near zero in some cases.[97] For instance, in a 2020 study of Pinus taeda in FACE plots, elevated CO2 buffered VPD effects on canopy conductance during moderate stress but failed to prevent hydraulic failure when VPD peaked above 3 kPa.[98]Empirical data from eddy covariance towers and satellite observations indicate that while CO2 fertilization has contributed to a 10-20% rise in global vegetation WUE since 1982, concurrent VPD increases have reduced terrestrial gross primary productivity by 5-10% in arid and semi-arid regions, highlighting regional variability.[99] Models incorporating these dynamics, such as those from the Community Land Model, project that without CO2 effects, VPD-driven water deficits would suppress biomass accumulation by up to 15% more than observed, underscoring the fertilizing role in countering aridity trends.[100] Nonetheless, in water-limited ecosystems like savannas, sustained high VPD may eventually overwhelm CO2 benefits if soil moisture recharge fails to match heightened leaf area from fertilization.[101]
Synergies and Conflicts with Temperature Changes
Elevated atmospheric CO2 often interacts antagonistically with warming temperatures on crop yields, where temperature-induced heat stress diminishes or negates the fertilization benefits. A meta-regression analysis of experimental data for major staples found that while CO2 elevation yields positive linear responses—such as +4% per 100 µmol mol⁻¹ for maize and rice, and +10% for soybean—warming imposes negative effects of -7.6% per °C for wheat, -9.5% for rice, and -9.5% for maize, ultimately reducing or eliminating net CO2-driven gains under projected climate scenarios.[53] Similarly, Free-Air CO2 Enrichment (FACE) simulations indicate that a 2°C temperature rise, accompanying CO2 increases to mid-century levels, could halve yields in crops like soybean and rice despite an 18% CO2 boost under optimal conditions, primarily through accelerated respiration, shortened grain-filling periods, and reproductive heat damage.[102]In combined stress scenarios, these conflicts intensify; for winter wheat under elevated CO2, warming, and water deficiency, biomass declined by 57% and leaf photosynthesis by 50%, reflecting synergistic negative impacts on stomatal conductance and enzyme function, though CO2 partially offset reductions in photosynthetic gene expression (e.g., +128% for RbcL3).[103] Such antagonism arises causally from temperature exceeding photosynthetic optima (typically 20–30°C for C3 crops), increasing maintenance respiration by 10–20% per °C and photorespiration losses, which elevated CO2 alone suppresses but cannot fully counteract under heat.[53]Synergistic benefits occur in select cases, particularly where CO2 enhances thermotolerance. In maize hybrids exposed to high temperatures, elevated CO2 ameliorated stress effects on physio-biochemical traits, sustaining growth and yield components better than warming alone, via improved water-use efficiency and reduced oxidative damage.[104] For woody species like Amur linden, combined elevated CO2 (750 µmol mol⁻¹) and +4°C warming boosted aboveground biomass, height, and leaf area significantly (P < 0.001), alongside higher photosynthetic nitrogen-use efficiency, despite lowered maximum carboxylation rates—indicating adaptive resource allocation that amplifies net productivity.[105] These positives stem from CO2-driven canopy cooling through transpiration and extended growing seasons in cooler baselines, though they are less pronounced in nutrient-limited or drought-prone systems.[103]Overall, empirical evidence from FACE and controlled trials underscores context-dependency: antagonistic interactions dominate in tropical/subtropical crops vulnerable to heat, while synergies may prevail in temperate forests or with breeding for heat resilience, highlighting the need for species-specific projections beyond isolated CO2 effects.[53][102]
Controversies and Scientific Debates
Discrepancies Between Models and Observations
Observations from Free-Air CO2 Enrichment (FACE) experiments indicate that elevated CO2 levels typically enhance net primary productivity (NPP) by 10-20% in forests and crops at concentrations around 550 ppm, but these gains often diminish over time due to nutrient constraints, particularly nitrogen and phosphorus limitations, which are not fully captured in many ecosystem models.[85][106] For instance, in the Duke FACE experiment with loblolly pines, initial NPP increases under elevated CO2 were sustained but constrained by nitrogen availability, leading to slower-than-predicted carbon sequestration in models lacking dynamic nutrient feedbacks.[85]Global satellite observations reveal a pronounced greening trend since the 1980s, with CO2 fertilization accounting for approximately 70% of the increase in leaf area index (LAI), yet process-based models simulate weaker or less spatially consistent responses, underestimating the fertilization effect by up to a factor of two when compared to inferred historical photosynthesis gains of 30% since 1900.[107][108] Conversely, recent analyses (post-2000) show a declining CO2 fertilization effect (CFE) on vegetationphotosynthesis, with observations indicating a stronger slowdown—potentially due to nutrient saturation and rising temperatures—than the milder decline projected by carbon cycle models, which may inadequately represent soil nutrient dynamics or vapor pressure deficit interactions.[8][109]In phosphorus-limited systems, carbon-phosphorus cycle models generally overestimate CO2-driven carbon sequestration by failing to account for observed stoichiometric imbalances, where experimental data demonstrate reduced phosphorus availability under elevated CO2 hampers predicted productivity gains.[106] These model-observation gaps highlight limitations in parameterizing feedbacks like nutrient retranslocation and microbial competition, with FACE syntheses underscoring that unfertilized field conditions yield lower CFE magnitudes (e.g., 12% for C3 crops) than model assumptions of unconstrained growth.[3] Addressing such discrepancies requires integrating empirical nutrient constraints into Earth system models to better align simulations with decadal-scale observations.[110]
Debates on Long-Term Sustainability
Long-term sustainability of the CO2 fertilization effect remains debated, with empirical evidence from Free-Air CO2 Enrichment (FACE) experiments indicating initial boosts in plant productivity that often diminish due to photosynthetic acclimation and resource constraints. In FACE studies spanning up to two decades, elevated CO2 consistently increased net primary production in forests and crops, yet this was accompanied by downregulation of photosynthetic capacity, evidenced by reductions in maximum carboxylation rate (Vcmax) by 10-20% after sustained exposure.[47][111] For instance, the Duke FACE experiment on loblolly pine forests showed sustained woody biomass accumulation under elevated CO2 from 1996 to 2010, but leaf-level photosynthesis acclimated, limiting further gains without additional inputs.[49]Nutrient limitations, particularly nitrogen and phosphorus, emerge as primary barriers to prolonged benefits, as faster growth under elevated CO2 dilutes tissue nutrient concentrations and depletes soil reserves. Satellite observations and modeling from 1982 to 2015 reveal a global decline in the CO2 fertilization effect on vegetationphotosynthesis, attributed to falling foliar nitrogen levels and soil water availability, with the effect halving in some regions.[8] In cropland FACE trials, rice yields increased by 14-35% under +200 ppm CO2 over multiple seasons, but high-yield cultivars showed greater acclimation, suggesting diminishing returns without fertilization to offset nutrient drawdown.[51] Critics argue this implies unsustainability in nutrient-poor ecosystems, where CO2-driven growth could eventually stall, as projected in phosphorus-limited tropical forests.[112]Proponents of sustained effects highlight synergies with improved water-use efficiency, which may extend benefits in semi-arid areas, though interactions with warming and drought complicate outcomes. Long-term FACE data on soybeans and wheat indicate that while acclimation reduces photosynthetic rates by 10-15%, overall biomass and yield gains persist for 5-10 years under managed conditions, challenging claims of rapid saturation.[113] However, unfertilized systems exhibit stronger downregulation, with leaf nitrogen dropping 5-10% per decade of exposure, raising concerns over ecosystem-level carbon sequestration efficacy.[114] These findings underscore that sustainability hinges on site-specific factors, with empirical FACE results tempering model-based optimism for indefinite greening.[8]
Role in Mitigating or Exacerbating Climate Effects
The CO2 fertilization effect primarily mitigates climate change by enhancing terrestrial carbon sequestration, as elevated atmospheric CO2 concentrations stimulate photosynthesis, leading to increased net primary productivity and biomass accumulation across ecosystems. Empirical data from global eddy covariance flux towers, spanning diverse biomes, demonstrate a robust fertilization response, with CO2 responsible for approximately 70% of the observed increase in gross primary production over recent decades. This effect has contributed to a detectable terrestrial carbon sink, absorbing an estimated 25-30% of anthropogenic CO2 emissions annually, thereby slowing the rate of atmospheric CO2 buildup and associated radiative forcing. Satellite observations further confirm widespread greening, particularly in drylands, where CO2-driven enhancements in water-use efficiency have expanded vegetation cover and bolstered carbon uptake under aridifying conditions.[37][9][36]However, interactions with concurrent climate stressors can limit or reverse this mitigating role, potentially exacerbating net warming. Recent analyses indicate a global decline in the fertilization effect's potency since the 1980s, with land ecosystems exhibiting reduced CO2 uptake efficiency—absorbing roughly 7% less per unit of productivity—due to rising temperatures, vapor pressure deficits, and nutrient constraints that diminish photosynthetic capacity over time. In northern mid-to-high latitudes, the initial positive indirect effects of elevated CO2 on vegetation carbon uptake have transitioned to negative since around 2000, as warming-induced respiration and drought override gains, leading to diminished sink strength. Models incorporating these dynamics project that without nutrient replenishment, the fertilization-driven carbon storage increase could be offset by climate feedbacks, such as enhanced soil carbon decomposition, resulting in a net positive contribution to atmospheric CO2 under high-emission scenarios.[8][115][116]Furthermore, while the effect improves plant resilience to drought in isolation, amplified heatwaves and altered precipitation patterns under climate change can negate these benefits, fostering ecosystem shifts—such as toward less efficient species compositions—that reduce long-term sequestration potential and may indirectly exacerbate warming through diminished albedo regulation or increased wildfire vulnerability in fertilized forests. Observations from free-air CO2 enrichment experiments underscore that sustained exposure leads to acclimation, where photosynthetic gains plateau, highlighting the transient nature of mitigation absent compensatory factors like nitrogen deposition. Overall, the net climate impact hinges on the balance between fertilization-enhanced sinks and overriding biophysical feedbacks, with empirical trends suggesting diminishing returns as global temperatures rise beyond 1.5°C.[117][53][109]
Projections and Future Implications
Model-Based Forecasts
Earth system models (ESMs) and dynamic global vegetation models (DGVMs) forecast that the CO2 fertilization effect will enhance terrestrial gross primary productivity (GPP) and biomass accumulation through the 21st century, driven by increased carboxylation efficiency and stomatal conductance reduction in the Farquhar-von Caemmerer-Berry photosynthesis model framework commonly implemented in these simulations. Multi-model ensembles from CMIP6 project that rising atmospheric CO2 concentrations could contribute 20-50% to global GPP increases by 2100 under SSP2-4.5 scenarios, with the fertilization effect dominating early-century gains before nutrient and climate feedbacks modulate responses.[8][118] However, DGVMs incorporating nitrogen cycle dynamics estimate a 25-30% lower land carbon storage response to CO2 fertilization compared to unconstrained models, highlighting nutrient limitations as a key damper on projected benefits.[119]For agricultural systems, process-based crop models calibrated with free-air CO2 enrichment (FACE) experiments forecast yield enhancements primarily for C3 crops, with wheat and rice projections showing 10-20% increases from CO2 alone by mid-century under elevated concentrations of 550 ppm.[120]Maize, a C4 crop, exhibits smaller modeled gains of 0-10% due to saturation of the CO2-concentrating mechanism, though water-use efficiency improvements benefit drought-prone regions.[121] Ensemble simulations indicate that CO2 fertilization offsets 20-50% of yield losses from concurrent warming and ozone exposure in high-emission pathways, potentially stabilizing global production for staples like soybeans and sorghum.[122][53]Uncertainties in these forecasts stem from inter-model variability in parameterizing beta factors (sensitivity of photosynthesis to CO2) and from divergences with observational data, where satellite-derived trends suggest weaker historical fertilization than ESMs imply, possibly indicating over-optimistic future projections without adjustments for declining marginal returns.[123] Constraining models with eddy covariance flux data yields higher inferred beta values (up to 0.47% GPP increase per ppm CO2), projecting sustained but regionally heterogeneous enhancements, strongest in nutrient-replete mid-latitudes.[108] Overall, while models consistently predict positive direct effects, integrated assessments under SSP5-8.5 foresee net terrestrial carbon uptake amplification by 2-5 PgC/year from fertilization by 2100, tempered by land-use change and warming interactions.[109]
Potential Under Varied Climate Scenarios
The magnitude of the CO2 fertilization effect (CFE) on global vegetation productivity is projected to diminish under higher warming scenarios due to compounding stresses from elevated temperatures and altered precipitation patterns. In low-emissions pathways such as Shared Socioeconomic Pathway (SSP) 1-1.9, which limit global warming to approximately 1.5°C by 2100, models indicate that CFE could enhance net primary productivity (NPP) by 10-20% through improved water-use efficiency and photosynthetic rates, with minimal offsetting from heat stress.[124] Conversely, under high-emissions SSP 5-8.5 scenarios projecting 4-5°C warming, temperature-induced respiration increases and drought frequency are expected to reduce CFE benefits by 30-50%, potentially leading to net declines in vegetation carbon uptake in tropical and temperate regions after mid-century.[8][116]Crop-specific responses further highlight scenario-dependent outcomes. For C3 crops like wheat and rice, CFE is forecasted to partially offset yield losses from ozone exposure and warming in Representative Concentration Pathway (RCP) 4.5 (moderate emissions, ~2.5°C warming), boosting yields by up to 15% relative to no-CFE simulations, but this amelioration weakens under RCP 8.5 where heat extremes negate gains, resulting in 5-10% net yield reductions.[122] C4 crops such as maize exhibit limited CFE responsiveness inherently, with projections showing near-total negation of any modest gains under warming above 2°C due to heightened vapor pressure deficits and evapotranspiration demands.[53] These interactions underscore that while CFE provides a temporary buffer in milder scenarios, its efficacy erodes in hotter, drier futures, as evidenced by dynamic global vegetation models incorporating leaf-to-canopy scaling.[108]Regional variations amplify these global trends. In semi-arid drylands, which cover 40% of Earth's land surface, SSP-based projections suggest sustained greening from CFE through enhanced stomatal conductance and reduced transpiration losses, even under 3°C warming, potentially increasing biomass by 20-30% by 2100.[68] However, boreal and tropical forest biomes face heightened risks in high-warming scenarios, where nutrient limitations and fire disturbances could cap CFE at 5-10% NPP gains before shifting to carbon source dynamics post-2050.[116] Empirical calibrations of Earth system models against satellite-derived leaf area index trends confirm that recent observational declines in CFE sensitivity—attributed to concurrent warming—align with projections for intensified climate interactions, emphasizing the need for scenario-specific parameterizations beyond static beta factors.[8][108]