Future anticipated warming could reduce the terrestrial carbon sink by ~50% by mid-century.
Abstract
The temperature dependence of global photosynthesis and respiration determine land carbon sink strength. While the land sink currently mitigates ~30% of anthropogenic carbon emissions, it is unclear whether this ecosystem service will persist and, more specifically, what hard temperature limits, if any, regulate carbon uptake. Here, we use the largest continuous carbon flux monitoring network to construct the first observationally derived temperature response curves for global land carbon uptake. We show that the mean temperature of the warmest quarter (3-month period) passed the thermal maximum for photosynthesis during the past decade. At higher temperatures, respiration rates continue to rise in contrast to sharply declining rates of photosynthesis. Under business-as-usual emissions, this divergence elicits a near halving of the land sink strength by as early as 2040.
INTRODUCTION
The difference between gross primary productivity, carbon uptake by vegetation, and total ecosystem respiration, carbon loss to the atmosphere, comprises the metabolic component of the land carbon sink [net ecosystem productivity (NEP)]. To date, land ecosystems provide a climate regulation service by absorbing ~30% of anthropogenic emissions annually [mean ± 1 SD: 2.6 petagrams carbon (PgC) ± 0.8 year−1] (1). While temperature functions as a key driver of year-to-year changes in the land carbon sink (2), its temperature response is still poorly constrained at biome to global scales (3, 4), making the carbon consequences of anticipated warming uncertain.
Like all biological processes, metabolic rates for photosynthesis and respiration are temperature dependent; they accelerate with increasing temperature, reach a maximum rate, and decline thereafter. Yet, these carbon fluxes do not necessarily have the same temperature response, potentially resulting in sharp divergences in ecosystem carbon balance. For example, increasing respiration rates without corresponding increases in photosynthesis rates would decrease the efficacy of the terrestrial carbon sink. An observational constraint on the net difference in metabolic response across both gross fluxes is thus urgently needed to constrain projections of the future land carbon sink and, more specifically, isolate points of nonlinear and perhaps nonreversible change—tipping points (5). This is especially relevant given the highly divergent land carbon sink trajectories from Earth system models (4) that, nevertheless, agree on continued future increases in sink strength due to the CO2 fertilization effect (3).
Given in situ evidence that regions of the terrestrial biosphere are experiencing temperature thresholds at which they switch from a carbon sink to source (6–8), we asked the following questions: (i) What are the thermal maxima of photosynthesis and respiration at biome to global scales? (ii) What is the thermal maximum for the land sink of carbon and current mean temperature range with regard to this critical threshold? (iii) At what global and regional temperatures do we expect the land sink of carbon to decline? (iv) Are those temperatures in the foreseeable future?
To address these questions, we used measurements from the largest continuous carbon monitoring network, FLUXNET (9), as an observational constraint to determine the temperature dependence of global rates of photosynthesis and respiration. Across ~1500 site years of daily data from all major biomes and plant functional types, we applied a 30-day moving window partial correlation analysis at each flux tower site to extract the temperature signal (a change in photosynthesis or respiration solely attributable to changes in temperature, i.e., the signal excludes other climatic effects such as water availability and sunlight) from daytime partitioned gross primary productivity [photosynthesis (P)] and total ecosystem respiration (R). We then normalized each site-level temperature dependence curve and applied macromolecular rate theory (MMRT) (10) in conjunction with Monte Carlo resampling to avoid length-of-record bias. The curves were subsequently aggregated to the biome level and then area-weighted to arrive at a global constraint of temperature dependence (see Materials and Methods). MMRT is a framework rooted in the principles of thermodynamics, which provides a mechanistic basis to extract the temperature dependence of rates across scales from individual enzyme kinetics to organismal and ecosystem metabolism (see Materials and Methods) (11). This framework is based on classical transition state theory from physical chemistry (12) and describes temperature rate dependence using three parameters, with emphasis on a maximum or optimal temperature value, Tmax, above which rates decline exponentially. The Arrhenius function is a special case of MMRT where the heat capacity term is zero and the temperature-rate relationship is exponential without a maximum (see Materials and Methods) (10). MMRT is applicable across a range of processes and levels of biological organization and has been successfully used to model the temperature dependence of enzyme kinetics (13), microbial growth (14), soil respiration (15), and leaf respiration (16). Here, we extend this analysis to include global land photosynthesis and net carbon fluxes, producing the first observationally derived curves for the temperature dependence of global carbon metabolism, using a single function grounded in thermodynamics.
Definitions: |
Temperature signal: A change in photosynthesis or respiration solely attributable to changes in temperature, i.e., the signal excludes other climatic effects such as water availability and sunlight. |
Tipping point: This denotes the temperature threshold at which the global land surface will switch from a carbon sink to a carbon source when—due solely to temperature—photosynthesis is in exponential decline while respiration is in exponential increase. |
Thermal maxima: The thermal maximum (Tmax) represents the peak of the temperature dependence curve where any additional increase in temperature will decrease the metabolic rate of either photosynthesis or respiration. |
Warmest Quarter: Mean temperature of warmest quarter (3-month period) |
RESULTS
In FLUXNET, the temperature response of global photosynthesis shows distinct maxima () at 18° and 28°C for C3 and C4 plant systems, respectively (Fig. 1). While the maximum for C3 plants is lower than optima observed in leaf-level measurements (17, 18), our estimates validate lower estimates derived elsewhere at the ecosystem scale (19). Furthermore, our estimates are based on ambient temperature and total ecosystem CO2 exchange and so are more directly relevant to global predictions for warming, which track global mean surface temperature as opposed to leaf temperature. In general, leaf temperatures are both (i) highly variable at even the individual plant level and (ii) poorly constrained at Earth system scales, making ambient air temperature a more suitable metric for investigating future response. Moreover, the maximum that we report is derived from observations that are restricted to temperatures experienced by ecosystems rather than the broader range imposed in controlled environment studies.
In contrast to photosynthesis, respiration rates increase across the range of ambient temperatures observed by FLUXNET (up to 38°C) (9), with no evidence of or rate decline. Using MMRT on experimental manipulations of leaf and soil respiration—together, ~87% of total ecosystem respiration (20, 21)—demonstrates that the thermal maxima of leaf and soil respiration reside at ~60° and 70°C, respectively (15, 16). This is far above temperatures observed at tower sites (9) and any near-term projections under any warming scenario (22). The high thermal maxima of leaf and soil respiration from experimental data are in agreement with the exponential increase in rate observed within ambient temperature FLUXNET data (fig. S1 and see Materials and Methods) and far above those for C3 and C4 photosynthesis. Temperatures where photosynthesis begins to decline are concurrent with the steepest increase in respiration rates for all datasets considered (9, 15, 16). Small changes in temperature past this point show opposite trends in the rates of photosynthesis and respiration. The large disparity between Tmax values for photosynthesis and respiration (autotrophic and heterotrophic combined) implies that flux responses diverge at temperatures above and that the imbalance grows more pronounced as temperature increases.
With temperature dependencies of both gross fluxes, we use mass balance to derive the optimal temperature of net land carbon uptake and find that, currently, the mean temperature of the warmest quarter (3-month period) extends just past (blue curve, Fig. 2). Our observationally derived temperature dependence curves explain both the current substantial sink of the biosphere (23, 24) and documented episodes of rapid release of carbon to the atmosphere during high temperature extremes (6–8). Current climate mostly lies just below , i.e., where slight increases in temperature act as climate fertilization of land carbon uptake. Under anticipated warming—as foreshadowed by historical temperature extremes and coincident land carbon loss—however, more and more time will be spent above . Past this threshold, the land carbon balance will first weaken and ultimately reverse sign from carbon sink to carbon source.
This link between anticipated warming and declines in land carbon uptake is a function of differential responses of gross fluxes to temperature. At temperatures up to the inflection point for photosynthesis, respiration and photosynthesis are effectively “coupled”—both processes increase with increasing temperature, albeit at different rates. At temperatures above the inflection point for photosynthesis, however, these processes become increasingly “decoupled.” That is, the rate of increase slows for photosynthesis and, past , declines exponentially. Throughout this temperature range, respiration continues to increase exponentially. This decoupling acts to severely degrade the land carbon sink. It is important to note that the extension of the warmest quarter past at FLUXNET sites is largely a recent phenomenon. When separated across greater than two decades of FLUXNET observations, the mean temperature of the warmest quarter has increased by 1.8°C, pushing current climate space past global and thus into a regime of declining photosynthetic rates (see Materials and Methods). Given that the mean temperature of the warmest quarter currently extends just past estimates of , any additional warming will both move mean climate past the inflection point for photosynthesis, effectively slowing land carbon uptake, and increase the cumulative amount of time past , where photosynthesis is negatively affected. Simultaneously, the response of respiration would be nearly exponential (9, 14–16). This intersection (25°C) constitutes a powerful tipping point for the land sink of carbon and a formidable positive climatic feedback (Fig. 2).
Currently, less than 10% of the terrestrial biosphere experiences temperatures past , where land carbon uptake is degraded (Fig. 3A). For regions that do experience these temperatures, exposure is limited to 1 to 2 months or constitutes areas with sparse to no vegetation. Under business-as-usual emissions, by 2100, up to half of the terrestrial biosphere could experience temperatures past , a three- to fivefold increase, based on uncertainty in temperature projections, over current levels (Fig. 3, B and C). However, the impact of elevated temperatures on the land sink is more than a function of cumulative area. Biomes that cycle 40 to 70% of all terrestrial carbon (19) including the rainforests of the Amazon and Southeast Asia and the Taiga forests of Russia and Canada are some of the first to exceed biome-specific for half the year or more. This reduction in land sink strength is effectively front-loaded in that a 45% loss occurs by midcentury, with only an additional 5% loss by the end of the century (Fig. 3D). Furthermore, these estimates are conservative as they assume full recovery of vegetation after temperature stress and ignore patterns and lags in recovery (25).
DISCUSSION
Our findings demonstrate temperature limits for global photosynthesis rates and the terrestrial land sink as a whole. Despite two decades of FLUXNET observations and the warmest decade on record, we observed no evidence of acclimation in photosynthesis (see Materials and Methods and fig. S2). While it is possible that temperature adaptation could mitigate the size of this impact, given high daily, seasonal, and interannual variation in temperature, as opposed to uniform warming from experimental data, the likelihood of detecting acclimation is low. Furthermore, two decades is likely too short a period to see selection for genotypes with higher temperature tolerance, particularly in systems dominated by perennial plants (16–28). Given current proximity to with no acclimation observed, it is unlikely that acclimation will proceed with sufficient speed to compensate for temperature-induced declines (29).
Beyond acclimation, and despite an increase of ~40-ppmv (parts per million by volume) CO2 over the 1991–2015 FLUXNET record, we also observed no notable alteration in the magnitude of photosynthesis across the data record (fig. S3). We note that, on the basis of the solubility of CO2 as a function of temperature and pressure, leaf water affinity for CO2 is nearly unchanged across the data record (30). We therefore contend that, in contrast to any CO2 fertilization effect (3), anticipated higher temperatures associated with elevated CO2 could degrade land carbon uptake and that failure to account for this results in a gross overestimation of climate change mitigation provided by terrestrial vegetation. We note that future work accounting for the timing of photosynthetic activity (31), CO2 concentrations, and the solubility of CO2 as a function of temperature (30) will be essential to accurately predict the role of CO2 fertilization in the land sink of carbon (32).
The temperature tipping point of the terrestrial biosphere lies not at the end of the century or beyond, but within the next 20 to 30 years (Figs. 2 and 3, A to D). Given the temperature limits of land carbon uptake presented here, without mitigating warming, we will cross the temperature threshold of the most productive biomes by midcentury, after which the land sink will degrade to only ~50% of current capacity if adaptation does not occur. While biomes will eventually shift spatially in response to warming, this process is unlikely to be a smooth migration, but rather a rapid disturbance-driven loss of present biomes (with additional emissions of carbon to the atmosphere), followed by a slower establishment of biomes more suited to the emerging climate. Furthermore, the establishment of new biomes is unlikely to be complete without human intervention and will be limited by edaphic factors, especially nutrient availability. This further suggests that we are rapidly entering temperature regimes where biosphere productivity will precipitously decline and calls into question the future viability of the land sink, along with Intended Nationally Determined Contributions (INDCs) within the Paris Climate Accord, as these rely heavily on land uptake of carbon to meet pledges (33). In contrast to Representative Concentration Pathway 8.5 (RCP8.5), warming associated with scenario RCP2.6 could allow for near-current levels of biosphere productivity, preserving the majority land carbon uptake (~10 to 30% loss). Failure to implement agreements that meet or exceed limits in the Paris Accord could quantitatively alter the large and persistent terrestrial carbon sink, on which we currently depend to mitigate anthropogenic emissions of CO2 and therefore global environmental change.
MATERIALS AND METHODS
Macromolecular rate theory
MMRT is based on classic transition state theory that describes the temperature dependence of chemical reaction kinetics using statistical thermodynamics (6). A central tenant of MMRT is the explicit recognition of the change in heat capacity for enzyme-catalyzed rates, —the difference in heat capacity between the enzyme-substrate (ES) complex and the enzyme–transition state (E-TS) complex. The heat capacity for large macromolecules such as enzymes is a function of the distribution of vibrational modes for the system.
For MMRT, the heat capacity term is incorporated into the Eyring equation to give Eq. 1 below. The resultant signature of MMRT is a curved plot of rate versus temperature in the absence of denaturation. determines the curvature of such a plot, and an important component of is the change in the distribution of vibrational modes in each state along the reaction coordinate (ES and E-TS complexes) (34)
(1) |
Equation 1 (based on transition state theory) lies at the heart of MMRT. It describes the rate (k) in terms of the Boltzmann, Planck, and universal gas constants (kB, h, and R, respectively), absolute temperature (T), the transmission coefficient (κ), the change in enthalpy and entropy between ground and transition states at a reference temperature (T0), and the change in heat capacity between ES and E-TS complexes . Thus, the first derivative of MMRT quantifies the change in rate (k) relative to change in temperature (T), given in Eq. 2
(2) |
We have previously demonstrated that MMRT accurately describes the temperature dependence of biological rates at increasing levels of complexity [microbial growth rates (14), soil respiration (15), and plant respiration (16)]. This provides justification for using MMRT in for analysis of the temperature dependence of ecosystem fluxes in the FLUXNET dataset.
FLUXNET data and processing
As an observational dataset for the temperature dependence of land carbon fluxes, mean daily estimates of carbon fluxes and micrometeorological variables were retrieved from the FLUXNET 2015 synthesis dataset for all tier 1 and tier 2 sites, along with uncertainty estimates based on gap filling and SD of fluxes (35). The daytime partitioning algorithm was selected for estimates of gross primary productivity (P) and total ecosystem respiration (R) to minimize bias associated with constraining the temperature response of partitioned fluxes through nighttime temperatures (36). Concurrent estimates of air temperature, latent and sensible heat, and downwelling short-wave radiation flux were also extracted, along with metrics for gapfilling of flux and meteorological data.
Combined, latent and sensible heat were used to calculate evaporative fraction (EF), the inverse of the Bowen ratio, and a robust index of relative water availability to the biosphere (Eq. 3) (37)
(3) |
where λE represents latent heat (watts per square meter) and H represents sensible heat (watts per square meter).
EF is an effective metric to assess water availability as it captures the signal from a multitude of potential water pools (e.g., soil moisture and precipitation) through evapotranspirative fluxes from the biosphere and scales well globally. We also evaluated the signal of vapor pressure deficit (VPD) as an alternate metric for water stress but found no statistically significant alteration of response (fig. S4). Given large variation in productivity and climate across biomes, we normalized all carbon fluxes along with micrometeorological variables within site to avoid signals based on biogeography. To maintain in situ derivation of temperature dependence, carbon flux and temperature data that were fully gap-filled were excluded from the analysis.
Temperature signal
Both photosynthesis and respiration are known to be controlled by a number of enviroclimatic variables, namely, sunlight, water, and temperature. To isolate the temperature signal, we used a 30-day moving-window partial correlation analysis on daily estimates of daytime partitioned gross primary productivity and total ecosystem respiration, with EF, downwelling short-wave radiation, and air temperature from 0° to 38°C (from biologically relevant temperatures for metabolic activity to the upper limit of the FLUXNET record) as explanatory variables at the individual site level, and filtered for significant relationships at P < 0.1. The result was the proportion of variation in gross fluxes that were solely attributable to each enviroclimatic variable. We then normalized and fit the temperature response of both fluxes by site to the first derivative of MMRT (11) to investigate changes in metabolism as a function of temperature (Eqs. 1 and 2). As MMRT was fitted at the site level and then bootstrapped, we filtered the FLUXNET synthesis dataset for towers that had a > 10 statistically attributed data points to ensure that data were sufficient to constrain temperature response curvature. Temperature projections from MMRT were limited to the ambient temperature window of observations from the FLUXNET record (0° to 38°C, the upper limit of FLUXNET observations).
Tmax or tipping point determination
Two important points exist within temperature dependence curves for biosphere metabolism: the inflection point (Tinf) and the thermal maximum (Tmax). The inflection point of temperature-dependent rates represents temperatures where an increase in rate (k) is maximal relative to temperature (T) and denotes where rates change from convex to concave. therefore represents the temperature at which land carbon uptake is maximal. The thermal maximum (Tmax) represents the top of the temperature dependence curve where any additional increase in temperature will decrease metabolic rate. Here, we define Tmax for the land sink as the mass balance difference between and .
Representativeness and uncertainty of FLUXNET data
Two major challenges exist for global constraint of biosphere metabolism using the FLUXNET dataset: (i) Observations are unequally distributed across the vegetated surface, with differing lengths of record, and (ii) because of the ambient and mixed-species nature of tower observations, the data are inherently noisy. The FLUXNET dataset, however, has been shown to be statistically representative of plant functional types and Koeppen-Geiger biomes globally, suggesting that statistical analyses leveraging FLUXNET observations are robust (38).
To address challenges (i) and (ii), we designed a bootstrap method that sampled entire tower records rather than observations (to avoid length of record bias) to fit global curves for the temperature dependence of land carbon fluxes. We then calculated the bootstrap-to-bootstrap variation in Tmax within Koeppen-Geiger biomes and across latitudes (fig. S2) to capture uncertainty stemming from sparse data sampling and heterogeneity of ecosystems sampled.
Bootstrapping and C3/C4 dichotomy
Early investigations into the temperature response of photosynthesis at global scales demonstrated a clear bimodal distribution that was well explained by C3 and C4 heuristics (39). All FLUXNET sites were therefore dichotomized into these two groups on the basis of climate criteria (40). The temperature response by group was then bootstrapped across the FLUXNET synthesis dataset 10,000 times, such that an entire site’s temperature curve was sampled rather than specific observations, thereby decreasing the length-of-record bias and unequal distribution across bioclimatic space of some long-lived sites.
Respiration temperature signal
The exponential Arrhenius-like response of total ecosystem respiration is largely a function of ambient temperature observations, where FLUXNET effectively samples temperatures far below for respiration constrained by experimental data (15, 16) and largely within the inflection point for this process (fig. S1). This behavior is in full agreement with MMRT, where, for values close to zero, MMRT predicts Arrhenius-like behavior. To give context for the disparity in Tmax between gross photosynthesis (P) and total ecosystem respiration (R) and to illustrate agreement between ambient temperature fitted FLUXNET data and wider-ranged experimental data, we incorporated two recent experiment-based respiration temperature response datasets (10, 11), which observe (fig. S1). The thermal maxima of leaf and soil respiration from these data reside at ~60° and 70°C, respectively, in alignment with ambient temperature FLUXNET predictions and far above either type of photosynthesis (fig. S1).
Evaluation of CO2 fertilization and VPD
To evaluate the effect of CO2 on the temperature dependence of gross primary production and the ability of CO2 fertilization to counter temperature-induced declines in land carbon uptake, we conducted a second moving-window partial correlation analysis that included ambient CO2 from FLUXNET towers with all other components remaining identical. While a ~1% increase in NEP per year has been correlated with elevated CO2 elsewhere in the literature (32), 90% confidence intervals of the temperature dependence signal with and without CO2 included showed no statistically significant difference (fig. S3). An identical model run was completed, replacing VPD with EF to evaluate potential changes in temperature response based on atmospheric demand rather than water flux, again demonstrating no significant differences (fig. S3).
Spatial gridding
To generate spatial grids of temperature response, FLUXNET sites were aggregated on the basis of Koeppen-Geiger climate classification regions where the FLUXNET synthesis dataset retained a coverage of >5 sites. We collapsed classes lacking sufficient replication to the next level of climatological organization. was then gridded spatially on the basis of Koeppen-Geiger climate classification (fig. S4).
Cumulative dose of temperature and fraction of vegetated surface in decline
Of interest for our work was the cumulative amount of mean monthly temperatures beyond within a given year. To measure this, we used FLUXNET-derived gridded , WorldClim 2 at 10-min spatial resolution for current climate and WorldClim 1.4 downscaled Coupled Model Intercomparison Project Phase 5 (CMIP5) data at 10-min spatial resolution (Fig. 3, A and B) (22), and CMIP5 monthly data for all RCP scenarios at 2.5° resolution (Fig. 3C). We then cumulatively tallied monthly mean temperature data that exceeded for both current and future climate datasets. On the basis of CMIP5 monthly data, we calculated the cumulative number of months beyond and weighted them by area to assess the fraction of terrestrial land sink in decline (Fig. 3C).
Decrease in biosphere productivity RCP8.5
As biosphere productivity varies spatially, we incorporated upscaled FLUXNET data to evaluate the impacts of exceedance of Tmax on total terrestrial biosphere productivity (38). To avoid biases stemming from interannual variability, we calculated mean biosphere productivity between 2003 and 2013 and evaluated temperature exceedance on the basis of our grid to evaluate the number of months that each grid cell is expected to be below or above this threshold for biosphere metabolism such that pixels, which were unaffected contributed full biome productivity estimates, and biomes, which spent the entire year beyond , contributed none.
Acclimation
To search for evidence of acclimation at the ecosystem-to-global scale, we first isolated FLUXNET tower sites that spanned both the first and second decades of the 2015 synthesis dataset. We then evaluated temperature dependence curves across both decades to look for upward shifts in (fig. S2). Although there is evidence elsewhere in the literature supporting a shift in thermal optima at higher temperatures for individual plants, we found no evidence of this acclimation at the ecosystem-to-global scale.
Data availability
FLUXNET data access depends on the tier of data used. Tier 1 data are open and free for scientific and educational purposes, and their use follows the fair use policy accessed at https://fluxnet.fluxdata.org/data/data-policy/. Tier 2 data are from producers who are currently unable to share their data in an open manner and require an approved proposal for data access. Data access proposal information can be found at https://fluxnet.fluxdata.org/. A list of FLUXNET sites from tiers 1 and 2 used in this analysis can be found in table S3. Downscaled WorldClim CMIP5 climate data used to evaluate future climate and therefore climate space beyond are freely available at http://worldclim.org/CMIP5v1. Upscaled FLUXNET data used to evaluate current and future biosphere productivity affected by temperature are freely available at www.fluxcom.org/.
Supplementary Material
Acknowledgments
We wish to acknowledge D. Huntzinger for support of this concept; C. Truettneter for WorldClim data support; K. Schmidt, M. Hurteau, and P. Fulé for feedback on framing; and D. Sonderegger for feedback on uncertainty analysis. This work used eddy covariance data acquired and shared by the FLUXNET community, including these networks: AmeriFlux, AfriFlux, AsiaFlux, CarboAfrica, CarboEuropeIP, CarboItaly, CarboMont, ChinaFlux, Fluxnet-Canada, GreenGrass, ICOS, KoFlux, LBA, NECC, OzFlux-TERN, TCOS-Siberia, and USCCC. The ERA-Interim reanalysis data are provided by ECMWF and processed by LSCE. The FLUXNET eddy covariance data processing and harmonization were carried out by the European Fluxes Database Cluster, AmeriFlux Management Project, and Fluxdata project of FLUXNET, with the support of CDIAC and ICOS Ecosystem Thematic Center, and the OzFlux, ChinaFlux, and AsiaFlux offices. Funding: Funding for this research was provided by the National Aeronautics and Space Administration (NASA) (grant NNX12AK12G), National Science Foundation (NSF) East-Asia Pacific Summer Institute Fellowship (1614404), Royal Society of New Zealand Foreign Partnership Programme (EAP-UOW1601), and New Zealand Marsden Fund (grant 16-UOW-027). Author contributions: K.A.D., C.R.S., V.L.A., and L.A.S. designed the analysis. K.A.D. carried out the analysis with support from L.L.L. K.A.D. wrote the manuscript with contributions from all authors. C.R.S. and G.W.K. contributed significantly to the framing of the paper. Competing interests: The authors declare that they have no competing interests. Data and materials availability: FLUXNET data access depends on the tier of data used. Tier 1 data are open and free for scientific and educational purposes, and their use follows the fair use policy accessed at https://fluxnet.fluxdata.org/data/data-policy/. Tier 2 data are from producers who are currently unable to share their data in an open manner and require an approved proposal for data access. Data access proposal information can be found at https://fluxnet.fluxdata.org/. A list of FLUXNET sites from tiers 1 and 2 can be found in the Supplementary Materials (table S3). Downscaled WorldClim CMIP5 climate data are freely available at http://worldclim.org/CMIP5v1. Upscaled FLUXNET data used to evaluate biosphere productivity are freely available at www.fluxcom.org/. An open repository with code used to fit MMRT along with parameters derived for each FLUXNET site used in this analysis are available at https://github.com/katharynduffy/TmaxLandUptake. Gridded generated from this analysis along with CMIP5 multimodel means, and gridded biosphere productivity, which is affected by are freely available at https://doi.pangaea.de/10.1594/PANGAEA.893266.
SUPPLEMENTARY MATERIALS
REFERENCES AND NOTES
- 1.Keenan T. F., Prentice I. C., Canadell J. G., Williams C. A., Wang H., Raupach M., Collatz G. J., Recent pause in the growth rate of atmospheric CO2 due to enhanced terrestrial carbon uptake. Nat. Commun. 7, 13428 (2016). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 2.Schneising O., Reuter M., Buchwitz M., Heymann J., Bovensmann H., Burrows J. P., Terrestrial carbon sink observed from space: Variation of growth rates and seasonal cycle amplitudes in response to interannual surface temperature variability. Atmos. Chem. Phys. 14, 133–141 (2014). [Google Scholar]
- 3.Huntzinger D. N., Michalak A. M., Schwalm C., Ciais P., King A. W., Fang Y., Schaefer K., Wei Y., Cook R. B., Fisher J. B., Hayes D., Huang M., Ito A., Jain A. K., Lei H., Lu C., Maignan F., Mao J., Parazoo N., Peng S., Poulter B., Ricciuto D., Shi X., Tian H., Wang W., Zeng N., Zhao F., Uncertainty in the response of terrestrial carbon sink to environmental drivers undermines carbon-climate feedback predictions. Sci. Rep. 7, 4765 (2017). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 4.Friedlingstein P., Meinshausen M., Arora V. K., Jones C. D., Anav A., Liddicoat S. K., Knutti R., Uncertainties in CMIP5 climate projections due to carbon cycle feedbacks. J. Climate 27, 511–526 (2013). [Google Scholar]
- 5.Lenton T. M., Held H., Kriegler E., Hall J. W., Lucht W., Rahmstorf S., Schellnhuber H. J., Tipping elements in the Earth’s climate system. Proc. Natl. Acad. Sci. U.S.A. 105, 1786–1793 (2008). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Ciais P., Reichstein M., Viovy N., Granier A., Ogée J., Allard V., Aubinet M., Buchmann N., Bernhofer C., Carrara A., Chevallier F., de Noblet N., Friend A. D., Friedlingstein P., Grünwald T., Heinesch B., Keronen P., Knohl A., Krinner G., Loustau D., Manca G., Matteucci G., Miglietta F., Ourcival J. M., Papale D., Pilegaard K., Rambal S., Seufert G., Soussana J. F., Sanz M. J., Schulze E. D., Vesala T., Valentini R., Europe-wide reduction in primary productivity caused by the heat and drought in 2003. Nature 437, 529–533 (2005). [DOI] [PubMed] [Google Scholar]
- 7.van Gorsel E., Wolf S., Cleverly J., Isaac P., Haverd V., Ewenz C., Arndt S., Beringer J., Resco de Dios V., Evans B. J., Griebel A., Hutley L. B., Keenan T., Kljun N., Macfarlane C., Meyer W. S., McHugh I., Pendall E., Prober S. M., Silberstein R., Carbon uptake and water use in woodlands and forests in southern Australia during an extreme heat wave event in the “Angry Summer” of 2012/2013. Biogeosciences 13, 5947–5964 (2016). [Google Scholar]
- 8.Guerlet S., Basu S., Butz A., Krol M., Hahne P., Houweling S., Hasekamp O. P., Aben I., Reduced carbon uptake during the 2010 Northern Hemisphere summer from GOSAT. Geophys. Res. Lett. 40, 2378–2383 (2013). [Google Scholar]
- 9.fluxdata.org, Data Processing (http://fluxnet.fluxdata.org//data/fluxnet2015-dataset/data-processing/), vol. 2018.
- 10.Arcus V. L., Prentice E. J., Hobbs J. K., Mulholland A. J., van der Kamp M. W., Pudney C. R., Parker E. J., Schipper L. A., On the temperature dependence of enzyme-catalyzed rates. Biochemistry 55, 1681–1688 (2016). [DOI] [PubMed] [Google Scholar]
- 11.Schipper L. A., Hobbs J. K., Rutledge S., Arcus V. L., Thermodynamic theory explains the temperature optima of soil microbial processes and high Q10 values at low temperatures. Glob Change Biol. 20, 3578–3586 (2014). [DOI] [PubMed] [Google Scholar]
- 12.Hobbs J. K., Jiao W., Easter A. D., Parker E. J., Schipper L. A., Arcus V. L., Change in heat capacity for enzyme catalysis determines temperature dependence of enzyme catalyzed rates. ACS Chem. Biol. 8, 2388–2393 (2013). [DOI] [PubMed] [Google Scholar]
- 13.Prentice E. J., Hicks J., Ballerstedt H., Blank L. M., Liáng L. L., Schipper L. A., Arcus V. L., The inflection point hypothesis: The relationship between the temperature dependence of enzyme-catalyzed reaction rates and microbial growth rates. Biochemistry 59, 3562–3569 (2020). [DOI] [PubMed] [Google Scholar]
- 14.Alster C. J., Baas P., Wallenstein M. D., Johnson N. G., von Fischer J. C., Temperature sensitivity as a microbial trait using parameters from macromolecular rate theory. Front. Microbiol. 7, 1821 (2016). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Robinson J. M., O’Neill T. A., Ryburn J., Liang L. L., Arcus V. L., Schipper L. A., Rapid laboratory measurement of the temperature dependence of soil respiration and application to changes in three diverse soils through the year. Biogeochemistry 133, 101–112 (2017). [Google Scholar]
- 16.Liang L. L., Arcus V. L., Heskel M. A., O’Sullivan O. S., Weerasinghe L. K., Creek D., Egerton J. J. G., Tjoelker M. G., Atkin O. K., Schipper L. A., Macromolecular rate theory (MMRT) provides a thermodynamics rationale to underpin the convergent temperature response in plant leaf respiration. Glob. Chang. Biol. 24, 1538–1547 (2018). [DOI] [PubMed] [Google Scholar]
- 17.Crafts-Brandner S. J., Salvucci M. E., Rubisco activase constrains the photosynthetic potential of leaves at high temperature and CO2. Proc. Natl. Acad. Sci. U.S.A. 97, 13430–13435 (2000). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Farquhar G. V., von Caemmerer S., Berry J. A., A biochemical model of photosynthetic CO2 assimilation in leaves of C3 species. Planta 149, 78–90 (1980). [DOI] [PubMed] [Google Scholar]
- 19.Huang M., Piao S., Ciais P., Peñuelas J., Wang X., Keenan T. F., Peng S., Berry J. A., Wang K., Mao J., Alkama R., Cescatti A., Cuntz M., de Deurwaerder H., Gao M., He Y., Liu Y., Luo Y., Myneni R. B., Niu S., Shi X., Yuan W., Verbeeck H., Wang T., Wu J., Janssens I. A., Air temperature optima of vegetation productivity across global biomes. Nat. Ecol. Evol. 3, 772–779 (2019). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Ryan M. G., Law B. E., Interpreting, measuring, and modeling soil respiration. Biogeochemistry 73, 3–27 (2005). [Google Scholar]
- 21.Atkin O. K., Bloomfield K. J., Reich P. B., Tjoelker M. G., Asner G. P., Bonal D., Bönisch G., Bradford M. G., Cernusak L. A., Cosio E. G., Creek D., Crous K. Y., Domingues T. F., Dukes J. S., Egerton J. J. G., Evans J. R., Farquhar G. D., Fyllas N. M., Gauthier P. P. G., Gloor E., Gimeno T. E., Griffin K. L., Guerrieri R., Heskel M. A., Huntingford C., Ishida F. Y., Kattge J., Lambers H., Liddell M. J., Lloyd J., Lusk C. H., Martin R. E., Maksimov A. P., Maximov T. C., Malhi Y., Medlyn B. E., Meir P., Mercado L. M., Mirotchnick N., Ng D., Niinemets Ü., O’Sullivan O. S., Phillips O. L., Poorter L., Poot P., Prentice I. C., Salinas N., Rowland L. M., Ryan M. G., Sitch S., Slot M., Smith N. G., Turnbull M. H., VanderWel M. C., Valladares F., Veneklaas E. J., Weerasinghe L. K., Wirth C., Wright I. J., Wythers K. R., Xiang J., Xiang S., Zaragoza-Castells J., Global variability in leaf respiration in relation to climate, plant functional types and leaf traits. New Phytol. 206, 614–636 (2015). [DOI] [PubMed] [Google Scholar]
- 22.Hijmans R. J., Cameron S. E., Parra J. L., Jones P. G., Jarvis A., Very high resolution interpolated climate surfaces for global land areas. Int. J. Climatol. 25, 1965–1978 (2005). [Google Scholar]
- 23.Pan Y., Birdsey R. A., Fang J., Houghton R., Kauppi P. E., Kurz W. A., Phillips O. L., Shvidenko A., Lewis S. L., Canadell J. G., Ciais P., Jackson R. B., Pacala S. W., McGuire A. D., Piao S., Rautiainen A., Sitch S., Hayes D., A large and persistent carbon sink in the world’s forests. Science 333, 988–993 (2011). [DOI] [PubMed] [Google Scholar]
- 24.Myneni R. B., Dong J., Tucker C. J., Kaufmann R. K., Kauppi P. E., Liski J., Zhou L., Alexeyev V., Hughes M. K., A large carbon sink in the woody biomass of Northern forests. Proc. Natl. Acad. Sci. U.S.A. 98, 14784–14789 (2001). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Schwalm C. R., Williams C. A., Schaefer K., Baldocchi D., Black T. A., Goldstein A. H., Law B. E., Oechel W. C., Scott R. L., Reduction in carbon uptake during turn of the century drought in western North America. Nat. Geosci. 5, 551 (2012). [Google Scholar]
- 26.Bertrand R., Lenoir J., Piedallu C., Riofrío-Dillon G., de Ruffray P., Vidal C., Pierrat J. C., Gégout J. C., Changes in plant community composition lag behind climate warming in lowland forests. Nature 479, 517–520 (2011). [DOI] [PubMed] [Google Scholar]
- 27.Corlett R. T., Westcott D. A., Will plant movements keep up with climate change? Trends Ecol. Evol. 28, 482–488 (2013). [DOI] [PubMed] [Google Scholar]
- 28.Zhu K., Woodall C. W., Clark J. S., Failure to migrate: Lack of tree range expansion in response to climate change. Glob. Chang. Biol. 18, 1042–1052 (2012). [Google Scholar]
- 29.Ghalambor C. K., McKay J. K., Carroll S. P., Reznick D. N., Adaptive versus non-adaptive phenotypic plasticity and the potential for contemporary adaptation in new environments. Funct. Ecol. 21, 394–407 (2007). [Google Scholar]
- 30.Weiss R., Carbon dioxide in water and seawater: The solubility of a non-ideal gas. Mar. Chem. 2, 203–215 (1974). [Google Scholar]
- 31.Toomey M., Friedl M. A., Frolking S., Hufkens K., Klosterman S., Sonnentag O., Baldocchi D. D., Bernacchi C. J., Biraud S. C., Bohrer G., Brzostek E., Burns S. P., Coursolle C., Hollinger D. Y., Margolis H. A., McCaughey H., Monson R. K., Munger J. W., Pallardy S., Phillips R. P., Torn M. S., Wharton S., Zeri M., Richardson A. D., Greenness indices from digital cameras predict the timing and seasonal dynamics of canopy-scale photosynthesis. Ecol. Appl. 25, 99–115 (2015). [DOI] [PubMed] [Google Scholar]
- 32.Peñuelas J., Ciais P., Canadell J. G., Janssens I. A., Fernández-Martínez M., Carnicer J., Obersteiner M., Piao S., Vautard R., Sardans J., Shifting from a fertilization-dominated to a warming-dominated period. Nat. Ecol. Evol. 1, 1438–1445 (2017). [DOI] [PubMed] [Google Scholar]
- 33.Forsell N., Turkovska O., Gusti M., Obersteiner M., den Elzen M., Havlik P., Assessing the INDCs’ land use, land use change, and forest emission projections. Carbon Balance Manag. 11, 26 (2016). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.van der Kamp M. W., Prentice E. J., Kraakman K. L., Connolly M., Mulholland A. J., Arcus V. L., Dynamical origins of heat capacity changes in enzyme-catalysed reactions. Nat. Commun. 9, 1–7 (2018). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 35.Papale D., Reichstein M., Aubinet M., Canfora E., Bernhofer C., Kutsch W., Longdoz B., Rambal S., Valentini R., Vesala T., Yakir D., Towards a standardized processing of Net Ecosystem Exchange measured with eddy covariance technique: Algorithms and uncertainty estimation. Biogeosciences 3, 571–583 (2006). [Google Scholar]
- 36.Lasslop G., Reichstein M., Papale D., Richardson A. D., Arneth A., Barr A., Stoy P., Wohlfahrt G., Separation of net ecosystem exchange into assimilation and respiration using a light response curve approach: Critical issues and global evaluation. Glob. Chang. Biol. 16, 187–208 (2010). [Google Scholar]
- 37.Schwalm C. R., Williams C. A., Schaefer K., Arneth A., Bonal D., Buchmann N., Chen J., Law B. E., Lindroth A., Luyssaert S., Assimilation exceeds respiration sensitivity to drought: A FLUXNET synthesis. Glob. Change Biol. 16, 657–670 (2010). [Google Scholar]
- 38.Jung M., Koirala S., Weber U., Ichii K., Gans F., Camps-Valls G., Papale D., Schwalm C., Tramontana G., Reichstein M., The FLUXCOM ensemble of global land-atmosphere energy fluxes. Sci. Data. 6, 1–14 (2019). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39.Still C. J., Berry J. A., Collatz G. J., DeFries R. S., Global distribution of C3 and C4 vegetation: Carbon cycle implications. Glob. Biogeochem. Cycles. 17, 1006–1014 (2003). [Google Scholar]
- 40.Collatz G. J., Berry J. A., Clark J. S., Effects of climate and atmospheric CO2 partial pressure on the global distribution of C4 grasses: Present, past, and future. Oecologia 114, 441–454 (1998). [DOI] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
FLUXNET data access depends on the tier of data used. Tier 1 data are open and free for scientific and educational purposes, and their use follows the fair use policy accessed at https://fluxnet.fluxdata.org/data/data-policy/. Tier 2 data are from producers who are currently unable to share their data in an open manner and require an approved proposal for data access. Data access proposal information can be found at https://fluxnet.fluxdata.org/. A list of FLUXNET sites from tiers 1 and 2 used in this analysis can be found in table S3. Downscaled WorldClim CMIP5 climate data used to evaluate future climate and therefore climate space beyond are freely available at http://worldclim.org/CMIP5v1. Upscaled FLUXNET data used to evaluate current and future biosphere productivity affected by temperature are freely available at www.fluxcom.org/.