Terrestrial ecosystems carbon and water cycles are tightly coupled through photosynthesis and evapotranspiration processes. The ratios of carbon stored to carbon uptake and water loss to carbon gain are key ecophysiological indicators essential to assess the magnitude and response of the terrestrial plant to the changing climate. Here, we use estimates from 10 terrestrial ecosystem models to quantify the impacts of climate, atmospheric CO2 concentration, and nitrogen (N) deposition on water use efficiency (WUE), and carbon use efficiency (CUE). We find that across models, WUE increases over the 20th Century particularly due to CO2 fertilization and N deposition and compares favorably to experimental studies. Also, the results show a decrease in WUE with climate for the last 3 decades, in contrasts with up-scaled flux observations that demonstrate a constant WUE. Modeled WUE responds minimally to climate with modeled CUE exhibiting no clear trend across space and time. The divergence between simulated and observationally-constrained WUE and CUE is driven by modeled NPP and autotrophic respiration, nitrogen cycle, carbon allocation, and soil moisture dynamics in current ecosystem models. We suggest that carbon-modeling community needs to reexamine stomatal conductance schemes and the soil-vegetation interactions for more robust modeling of carbon and water cycles.
Terrestrial ecosystems assimilate atmospheric CO2 through photosynthesis, where carbon sequestered is accompanied by loss of water to the atmosphere as regulated by leaf stomata. The rate of net carbon uptake (net primary production, NPP) to gross carbon uptake (gross primary production, GPP) is referred to as carbon use efficiency (CUE). CUE plays an important role in the terrestrial ecosystem carbon balance1 and determines the amount of carbon allocated to biomass. An additional metric of plant resource economy quantifies the rate of carbon uptake per unit of water loss. This water use efficiency (WUE) is a key physiological parameter linking carbon and water cycles. WUE quantifies the amount of water that terrestrial ecosystems use relative to carbon gained2,3. CUE and WUE are important indicators of plants ability to adapt to changing environmental conditions, such as precipitation and temperature. Understanding changes in CUE and WUE is critical to quantify the response of terrestrial ecosystems to the changing climate4,5,6,7.
Variability in CUE and WUE efficiencies is a reflection of the ecosystem dynamics in a changing environment. Low CUE can be an indication of high respiratory cost associated with warmer temperature, longer growing season, and nutrient deficiencies1,8. High CUE can be an indication of adaptation to harsh environmental conditions such as cold temperature and insufficient precipitation9. High WUE can indicate low stomatal conductance resulting in reduced transpiration10, which is the case of plants growing in arid conditions. A low WUE can indicate sufficient soil moisture or precipitation and enhanced tree growth. Under a projected warming climate (hotter and drier environmental conditions., CUE is expected to decrease as respiratory cost increases11, while WUE is expected to increase due to reductions in stomatal conductance12, resulting in limited tree growth13,14,15,16.
The leaf ecophysiological properties indicate that CUE and WUE should increase due to increasing atmospheric CO2- known as “the CO2 fertilization effect”. CO2 enrichment experiments3,17,18, ecosystem models, isotope analysis19,20,21, and WUE model (WUE estimated independently from GPP and evapotranspiration)22, support an increase in plant WUE as atmospheric CO2 concentration increases. However, the response of CUE to changes in atmospheric CO2 levels is largely unknown leading to a debate about the role of nutrients limitations10,19. This is not surprising given the difficulties in estimating CUE at sites and the difficulties in extrapolating the limited CUE estimates from a local to a global scale. Understanding how the changing climate induces changes in WUE and CUE is of critical importance to improve our abilities to accurately predict any future ecosystem changes.
Here, we analyze trends in global CUE and WUE using an ensemble of ten ecosystem models (see Methods) from the Multi-scale Synthesis and the Terrestrial Model Intercomparison Project (MsTMIP)23. In order to achieve this, we use an “assumption-centered“ approach24 to identify key model processes related to estimating CUE and WUE and to evaluate the assumptions in these processes against published studies and the globally upscaled flux tower observations25. We focus on quantifying the long-term impacts of atmospheric CO2, climate change, and nitrogen deposition as well as their combined effects on annual modeled CUE and WUE. We address a variety of factors that can influence the models’ trend, including the potential role of autotrophic respiration and carbon allocation. Furthermore, the intermodel analysis focuses on determining the dominant environmental drivers of the modeled CUE and WUE. This allows for models’ structure to be assessed, while providing intercomparison of the modeled CUE and WUE driver’s spatial and temporal variability.
Results and Discussion
We find that models disagree in terms of the magnitude and trend of WUE and CUE, which reflects the differences in model structure and parameterization. The trend of the models’ WUE (positive trend) and CUE (some models showed a positive trend, while others showed a negative trend) is significant (Mann-Kendall p < 0.05) for CO2 fertilization and N deposition scenarios and shows contrasting results for the climate scenario with about half of the models showing no significant trend with time (Tables S1 and S2).
We compare the effects of the changing climate on modeled WUE (Fig. 1a) to FLUXNET-MTE for the period of 1982–2008 (Fig. S1). Only four models show a significant decreasing trend (Mann-Kendall p < 0.05) with a drop in carbon sequestered per unit of water lost (increase in leaf transpiration; see Methods) ranging between −1.4% to −25.6% for WUE, while the remaining models show no trend (Table S1). Meanwhile, no significant trend (p = 0.6) in FLUXNET-MTE WUE for the same period is detected (Fig. S1; Table S1). Discrepancies between models and FLUXNET-MTE is due to differences in the representation of soil hydrology and the interconnectedness of stomatal conductance and carbon assimilation between models. For example, CLM4 shows similar WUE values to FLUXNET-MTE with a mean absolute error of 0.04 gC/kgH2O, unlike CLM4VIC that underestimated FLUXNET-MTE WUE with a mean absolute error of 0.18 gC/kgH2O (Fig. S1). Implementation of VIC hydrology in CLM4 resulted in an increase in soil moisture and a decrease in WUE.
The differences we find in modeled CUE and WUE are due to models’ representation of the interactions between climate, atmospheric CO2 concentration, and N-deposition. Whether a model considers C-N coupling appears to influence WUE and CUE sensitivities to an increase in atmospheric CO2. On average, C-N models show a weaker WUE response to CO2 fertilization than C only models (Fig. 1b; Table S4). Models, with the exception of VEGAS2.1, predicted an increase in WUE due to CO2 fertilization (Table S4) consistent with observational studies that estimated an increase in WUE ranging from 8% to 35% over the 20th century10,12,15,17,26,27. This suggests a decrease in the models stomatal conductance with CO2 fertilization similar to observations15,20,26,28. Three of the C-N models (CLM4, CLM4VIC, and DLEM) also show a negative CUE response to CO2 fertilization (Fig. 2b; Table S2). Results show for models with positive CUE trend (Fig. 2b), such as ISAM, LPJ and ORCHIDEE, the percentage increase in NPP is considerably larger than the percentage increase in GPP (Table S5). Whereas, models that show negative CUE trend (Fig. 2b), such as CLM and CLMVIC, the percentage increases in NPP and GPP are the same or GPP percentage increase is greater than that of NPP (Table S5). This drastic response in models CUE is attributed in part to higher autotrophic respiration rates relative to NPP. In general, models’ autotrophic respiration structure is almost identical, but drivers of autotrophic respiration, such as carbon allocation scheme and tissue turnover vary between models. Models (e.g. CLM4 and CLMVIC) that are parameterized to favor increased tree growth (mainly wood biomass) risk increasing plant autotrophic respiration and decreasing CUE with CO2 fertilization (Table S3). In addition, the discrepancy between the models’ estimated WUE with climate change (Fig. 1a) can be due to either an increase in stomatal conductance or in photorespiration that leads to a decrease in GPP. Further experimentation is needed to modify model processes (e.g. carbon allocation and autotrophic respiration) that lead to near constant CUE with time to preserve the inter-annual and seasonal variability in CUE as observed in field studies29,30,31 and to accurately capture stomatal conductance response to changing environmental conditions to improve models’ prediction of the carbon and water cycles.
The differences in model response to N deposition can be traced to GPP-N relationships. Models showed a slight increase in WUE with N deposition between years 1901 and 2010 (Mann-Kendall p < 0.05) with a % change ranging from 0.07% to 0.8% (Table S1). This is similar to recent long-term studies that showed a slight increase in WUE (intrinsic WUE) with N deposition at site and regional scales32,33,34. On average models GPP increased by about 4% more than models evapotranspiration (0.5%), resulting in the apparent increase in models WUE with N deposition (Fig. 1c). In addition, CLM potential GPP is limited by N requirements for new tissue growth35,36 while in ISAM GPP is limited by N down regulation of Vcmax37. Thus, additional N resulted in a slight increase in NPP in CLM4 and CLM4VIC due to an increase in LAI (Fig. S2), while ISAM is less sensitive to N deposition. Moreover, ISAM CUE and WUE exhibit little to no effect by N deposition, suggesting that the carbon allocation scheme is not sensitive to N deposition and that the structural growth-N deposition relationship needs to be modified to improve the response of ISAM to N deposition (Fig. 2c). Nevertheless, all models show minimal impacts of N deposition on CUE. Thus, modifications of N deposition interactions with leaf N and Vcmax are recommended to improve model performance.
There is an agreement on the dominant drivers of WUE and CUE between models (Figs 3, 4 and S3). CO2 fertilization is the main driver for CUE and WUE changes in most models (Table S6). Our conclusion is similar to other studies that found models net carbon uptake is CO2 dependent and highly variable between LSMs27,38. However, N deposition is the main driver for two models (CLM4 and CLM4VIC) and climate is the main driver for one model (VEGAS2.1) (Figs 3, 4 and S3). The dominance of N deposition as the environmental driver of CLM4 and CLM4VIC can be an indication of the models strong N limitation because CO2 fertilization of GPP is calculated independent of N limitations and then downregulated if N uptake is insufficient to support GPP39. The dominance of CO2 fertilization as the main environmental drivers to WUE, CUE, GPP, and NPP is more consistent among C only models than C-N models (Figs 3, 4 and S4–6). It is possible that the difference between C-N and C only models is due to different model parametrizations and structure23, such as stomatal conductance scheme and whether stomatal conductance is parametrized for the whole canopy or sunlit/shaded leaves.
Models disagree on the spatial importance of all environmental drivers19 with low agreement in the temperate and the boreal-artic zones and high agreement in the tropical zone (Figs 3 and 4). In the arctic and boreal regions, models’ CUE and WUE are driven by atmospheric CO2 levels and, to a lesser extent, by the changing climate (Figs 3 and 4). This contrast studies showing that climate is the dominant contributor to the increase in intrinsic WUE in boreal forest in the last five decades21,40. Also, there is a significant disagreement for the dominance environmental drivers for topical Asia with three models (LPJ-wsl, ORCHIDEE- LSCE, and VEGAS2.1) showing climate as the important driver, unlike the rest of the models (Fig. 3). Nevertheless, we find that the spatial dominance of all environmental drivers of models CUE and WUE follows a similar spatial pattern to that of GPP and NPP (Figs S4 and S5). Whereas, climate is the dominate environmental driver of ET for almost all models (Fig. S6), but is not as prominent driver for models’ WUE. This is related to the fact that the % change in models’ GPP is much larger than that of ET (Table S5). The small effects of CO2 fertilization on ET is not due to differences in evapotranspiration scheme between models, but rather due to models assumptions that can lead to lower CO2 effects on ET (e.g. decoupling of assimilation and transpiration and whether soil moisture stress modifies assimilation and stomatal conductance). Models high sensitivity to CO2 fertilization and low sensitivity to climate (Figs 3, 4 and S2) is a result of indirect tuning of models sensitivities to environmental drivers38. We argue that autotrophic respiration and GPP schemes needs to be modified to improve their sensitivity to temperature and CO2 fertilization for better projection of the carbon sink magnitude under changing environmental conditions.
We find that latitudinal variability in soil moisture and temperature (Figs S7 and S8) is not directly related to that of CUE and WUE (Figs S9 and S10). For instance, CLM4 and GTEC soil moisture show a near constant response to climate and CO2 fertilization (Fig. S7a,b), unlike CLM4 and GTEC CUE and WUE (Figs S9 and S10). Even models with different soil hydrology (CLM4 and CLM4VIC) show similar CUE and WUE sensitives to environmental drivers (Figs S9 and S10). The low sensitivity of above ground processes to soil moisture and temperature suggest either inaccurate models assumptions or decoupling between soil moisture and CUE and WUE. We note that models soil temperature respond to climate driver (Fig. S8a) is consistent with the observed increase in soil temperature across the globe41,42,43,44,45. The decrease in models’ temperature (except LPJ-wsl and GTEC) due to CO2 fertilization (Fig. S8b) can reduce the effect of CO2 fertilization on CUE and WUE46, but such an affect is not apparent in models’ CUE and WUE (Figs S9 and S10). Nevertheless, accurate representation of soil hydrology and better assumptions about GPP-ET interactions47 are keys to improve models’ prediction of environmental drivers of terrestrial ecosystems.
Future studies need to investigate the soil-vegetation interactions and assumptions in ecosystem models and how such interactions/assumptions impact vegetation CUE and WUE. For instance, what is the role of soil moisture or water stress on model WUE? More information about model assumptions is needed to answer this question. However, it does seem that CO2 fertilization causes stomatal conductance to increase regardless of soil water availability. Moreover, carbon isotope studies suggest a constant ratio of intercellular CO2 (ci) and atmospheric CO2 (ca) [ci/ca ratio] with increasing atmospheric CO2 concentration15,18,48 and depending on temperature, vapor pressure deficit and elevation. Does this suggest that models with decreasing WUE due to CO2 fertilization are not maintaining a near constant ci/ca ratio? We hypothesize that this is the case in ecosystem models, but we know very little to nothing about the models ci/ca ratio to verify our hypothesis because ci/ca ratio is not a typical ecosystem models output.
Detailed analysis of ecosystem models CUE and WUE provides necessary information about model assumptions and parameterizations. On average, we find that models predict WUE more accurately and show contrasting results for CUE, particularly for climate change and nitrogen deposition scenarios. The uncertainties and errors in CUE can be mostly attributed to NPP and autotrophic respiration, nitrogen cycle, and carbon allocation schemes in current ecosystem models. Our analysis also suggests that ecosystem models should consider the acclimation of ecosystems to rise in temperature in order to increase the sensitivity of CUE to climate. Future model intercomparison studies24,47,48 should move beyond model results comparison and should seek to understand and identify the key processes that will lead to better model performance and will reduce uncertainties in the future projections. Key processes can be identified by: (1) Synthesis of existing data (e.g. turnover rates, allocation, soil temperature and moisture) to constrain and reduce models uncertainties; and (2) Comprehensive analysis of models behavior and validation at finer temporal scales (daily and diurnal cycle) for important variables (carbon and water fluxes as well as soil temperature and moisture) at multiple sites (e.g. FLUXNET sites) to pinpoint exact processes and parameters that require modification. We call on new intercomparison studies focus not only on vegetation variables (e.g. GPP, NPP, etc.), but also on soil physical and chemical properties (e.g. soil moisture and temperature) because it should not be expected that models would accurately predict the carbon and water cycles unless water stress and soil moisture are accurately captured.
The models used here are part of the Multi-Scale synthesis and Terrestrial Model Intercomparison Project (MsTMIP). To eliminate any errors that could arise between models due to the use of different environmental drivers, standardized forcing data such as climate, land cover, atmospheric CO2 concentration, and N deposition, were provided to the modelers. Models simulations are for the time period spanning 1901–2010 using a standard spin-up and simulation protocols39,49. The models are run in an offline simulation using the forcing data provided. Each simulation protocol is designed to test the sensitivity of one of the above-mentioned forcing data and the impact of each driver is calculated through simulation differencing as mentioned previously (Table S7). We only use the models that outputted GPP, NPP, autotrophic respiration, and evapotranspiration for all the simulations (Table S8). We note that evapotranspiration data are lacking for TEM6 and it is included only in the analysis of CUE.
The climate impact on modeled CUE and WUE is calculated as the difference between fixed and variable climate simulations (SG1-RG1); atmospheric CO2 concentration impacts on modeled CUE and WUE are calculated as the difference between fixed and variable atmospheric CO2 concentration simulations (SG3-SG2); and N-deposition impact on modeled CUE and WUE is calculated as the difference between fixed and variable N deposition simulations (BG1-SG3). The combined effects of climate and increases in atmospheric CO2 concentration and N-deposition are assessed by analyzing BG1 simulation. The models WUE for the SG1 simulation are compared to FLUXNET-MTE for years 1982–2008. We calculated the net change in WUE and CUE for the BG1 simulations as the difference between yearly WUE or CUE estimates and WUE or CUE estimates for year 1901 (net WUE[n] or CUE[n] = WUE[n] or CUE [n] – WUE or CUE, where n is year).
Mann-Kendall nonparametric test is applied to statistically detect any trend (increasing or decreasing) in WUE and CUE over time50,51. We use the trend free pre-whitening approach52 Mann-Kendall test to remove any correlation in the time series data as it has been shown to outperform the pre-whitening approach and reduce the errors in trend detection52,53. The null hypothesis (H0) of this test is no trend, and the alternative hypothesis (HA) that there is a trend. Mann-Kendall test ranges from −1 to 1 with values close to zero indicating no trend. Also, we use the Sen’s slope nonparametric methods to estimate the slope of the trend. Positive values of Sen’s slope indicate an increasing trend and negative values indicate a decreasing trend.
Calculation of magnitude change as percentage of mean
We calculate percentage change as the median slope (Sen’s slope for WUE or CUE) multiplied by the period length (n) divided by the mean54 as:
Calculation of N deposition effect on LAI: We calculated LAI for CLM4 and CLM4VIC because they provided LAI for the BG1 simulations (ISAM LAI for this version of MsTMIP is satellite-based and not dynamically estimated, thus it is excluded from this analysis). We limit the analysis for areas north of 25° latitude since these are the areas considered N limited. We extract LAI data for months of April to October and average the LAI for each of these months to produce a time series of LAI data for years 1901 until 2010.
Calculation of percentage changes in model data
We calculate the percentage increase in NPP, GPP, and autotrophic respiration for any simulation as the difference between 2010 and 1901 estimates. We calculate the percentage contribution of climate, CO2 fertilization, and N deposition to the models BG1 CUE and WUE estimates as the ratio between the average difference in simulations (e.g. SG1 - RG1) and average BG1 WUE and CUE for C-N models and SG3 WUE and CUE for C only models for year 1901–2010.
The output of MsTMIP models are available from https://daac.ornl.gov/cgi-bin/dsviewer.pl?ds_id=1225.
DeLucia, E. H., Drake, J. E., Thomas, R. B. & Gonzalez-Meler, M. Forest carbon use efficiency: is respiration a constant fraction of gross primary production? Global Change Biology 13, 1157–1167 (2007).
Tang, X. et al. How is water-use efficiency of terrestrial ecosystems distributed and changing on Earth? Scientific Reports 4, srep07483 (2014).
Keenan, T. F. et al. Increase in forest water-use efficiency as atmospheric carbon dioxide concentrations rise. Nature 499, 324–327 (2013).
Huang, M. et al. Seasonal responses of terrestrial ecosystem water-use efficiency to climate change. Global Change Biology 22, 2165–2177 (2016).
Huang, M. et al. Change in terrestrial ecosystem water use efficiency over the last three decades. Global Change Biology 21(6), 2366–2378 (2015).
Vicca, S. et al. Fertile forests produce biomass more efficiently. Ecology Letters 15, 520–526 (2012).
Leakey, A. D. B. et al. Elevated CO2 effects on plant carbon, nitrogen, and water relations: six important lessons from FACE. J Exp Bot 60, 2859–2876 (2009).
Zhang, Y., Xu, M., Chen, H. & Adams, J. Global pattern of NPP to GPP ratio derived from MODIS data: effects of ecosystem type, geographical location and climate. Global Ecology and Biogeography 18, 280–290 (2009).
Kim, D. et al. Intercomparison of Terrestrial Carbon Fluxes and Carbon Use Efficiency Simulated by CMIP5 Earth System Models. Biogeosciences Discuss. 2016, 1–50 (2016).
van der Sleen, P. et al. No growth stimulation of tropical trees by 150 years of CO2 fertilization but water-use efficiency increased. Nature Geosci 8, 24–28 (2015).
Zhang, Y. et al. Climate-driven global changes in carbon use efficiency. Global Ecology and Biogeography 23, 144–155 (2014).
Battipaglia, G. et al. Elevated CO2 increases tree-level intrinsic water use efficiency: insights from carbon and oxygen isotope analyses in tree rings across three forest FACE sites. New Phytol 197, 544–554 (2013).
Girardin, M. P. et al. No growth stimulation of Canada’s boreal forest under half-century of combined warming and CO2 fertilization. PNAS 113, E8406–E8414 (2016).
Lavigne, M. B. & Ryan, M. G. Growth and maintenance respiration rates of aspen, black spruce and jack pine stems at northern and southern BOREAS sites. Tree Physiol 17, 543–551 (1997).
Peñuelas, J., Canadell, J. G. & Ogaya, R. Increased water-use efficiency during the 20th century did not translate into enhanced tree growth. Global Ecology and Biogeography 20, 597–608 (2011).
Silva, L. C. R. & Horwath, W. R. Explaining Global Increases in Water Use Efficiency: Why Have We Overestimated Responses to Rising Atmospheric CO2 in Natural Forest Ecosystems? PLOS ONE 8, e53089 (2013).
Frank, D. C. et al. Water-use efficiency and transpiration across European forests during the Anthropocene. Nature Clim. Change 5, 579–583 (2015).
Ito, A. & Inatomi, M. Water-Use Efficiency of the Terrestrial Biosphere: A Model Analysis Focusing on Interactions between the Global Carbon and Water Cycles. J. Hydrometeor. 13, 681–694 (2011).
Giguère-Croteau, C. et al. North America’s oldest boreal trees are more efficient water users due to increased [CO2], but do not grow faster. Proceedings of the National Academy of Sciences 116, 2749–2754 (2019).
Xu, G. et al. Climate warming and increasing atmospheric CO2 have contributed to increased intrinsic water-use efficiency on the northeastern Tibetan Plateau since 1850. Trees 27, 465–475 (2013).
Xu, G. et al. Disentangling Contributions of CO2 Concentration and Climate to Changes in Intrinsic Water-Use Efficiency in the Arid Boreal Forest in China’s Altay Mountains. Forests 9, 642 (2018).
Cheng, L. et al. Recent increases in terrestrial carbon uptake at little cost to the water cycle. Nature Communications 8, https://doi.org/10.1038/s41467-017-00114-5 (2017).
Huntzinger, D. N. et al. The North American Carbon Program Multi-Scale Synthesis and Terrestrial Model Intercomparison Project – Part 1: Overview and experimental design. Geosci. Model Dev. 6, 2121–2133 (2013).
Medlyn, B. E. et al. Using ecosystem experiments to improve vegetation models. Nature Clim. Change 5, 528–534 (2015).
Jung, M. et al. Global patterns of land‐atmosphere fluxes of carbon dioxide, latent heat, and sensible heat derived from eddy covariance, satellite, and meteorological observations. Journal of Geophysical Research-Biogeosciences 116, G00J07, https://doi.org/10.1029/2010JG001566, (2011).
Lévesque, M., Siegwolf, R., Saurer, M., Eilmann, B. & Rigling, A. Increased water-use efficiency does not lead to enhanced tree growth under xeric and mesic conditions. New Phytol 203, 94–109 (2014).
Saurer, M. et al. Spatial variability and temporal trends in water-use efficiency of European forests. Glob Change Biol 20, 3700–3712 (2014).
Wu, G. et al. Long-term variation of tree growth and intrinsic water-use efficiency in Schrenk spruce with increasing CO2 concentration and climate warming in the western Tianshan Mountains, China. Acta Physiol Plant 37, 150 (2015).
Curtis, P. S. et al. Respiratory carbon losses and the carbon-use efficiency of a northern hardwood forest, 1999–2003. Tree Physiology 167, 437–456 (2005).
Zanotelli, D., Montagnani, L., Manca, G. & Tagliavini, M. Net primary productivity, allocation pattern and carbon use efficiency in apple orchard assessed by integrating eddy covariance, biometric and continuous soil chambers measurements. Biogeosciences 10, 3089–3108 (2013).
Schwalm, C. R., Black, A., Morgenstern, K. & Humphreys, E. R. A method for deriving net primary productivity and component respiratory fluxes from tower-based eddy covariance data: a case study using a 17-year data record from a Douglas-fir chronosequence. Global Change Biology 13, 370–385 (2007).
Guerrieri, R., Lepine, L., Asbjornsen, H., Xiao, J. & Ollinger, S. V. Evapotranspiration and water use efficiency in relation to climate and canopy nitrogen in U.S. forests. J. Geophys. Res. Biogeosci. 121, 2016JG003415 (2016).
Jennings, K. A., Guerrieri, R., Vadeboncoeur, M. A. & Asbjornsen, H. Response of Quercus velutina growth and water use efficiency to climate variability and nitrogen fertilization in a temperate deciduous forest in the northeastern USA. Tree Physiol 36, 428–443 (2016).
Leonardi, S. et al. Assessing the effects of nitrogen deposition and climate on carbon isotope discrimination and intrinsic water-use efficiency of angiosperm and conifer trees under rising CO2 conditions. Glob Change Biol 18, 2925–2944 (2012).
Lee, E., Felzer, B. S. & Kothavala, Z. Effects of nitrogen limitation on hydrological processes in CLM4-CN. J. Adv. Model. Earth Syst. 5, 741–754 (2013).
Oleson, K. et al. Technical description of version 4.5 of the Community Land Model (CLM), https://doi.org/10.5065/D6RR1W7M (2013).
El-Masri, B. et al. Carbon dynamics in the Amazonian Basin: Integration of eddy covariance and ecophysiological data with a land surface model. Agricultural and Forest Meteorology 182, 156–167 (2013).
Huntzinger, D. N. et al. Uncertainty in the response of terrestrial carbon sink to environmental drivers undermines carbon-climate feedback predictions. Scientific Reports 7, 4765 (2017).
Zaehle, S. et al. Evaluation of 11 terrestrial carbon–nitrogen cycle models against observations from two temperate Free-Air CO2 Enrichment studies. New Phytol 202, 803–822 (2014).
Saurer, M., Siegwolf, R. T. W. & Schweingruber, F. H. Carbon isotope discrimination indicates improving water-use efficiency of trees in northern Eurasia over the last 100 years. Global Change Biology 10, 2109–2120 (2004).
Fang, X., Luo, S. & Lyu, S. Observed soil temperature trends associated with climate change in the Tibetan Plateau, 1960–2014. Theor Appl Climatol 135, 169–181 (2019).
Hu, Q. & Feng, S. A Daily Soil Temperature Dataset and Soil Temperature Climatology of the Contiguous United States. J. Appl. Meteor. 42, 1139–1156 (2003).
Jungqvist, G., Oni, S. K., Teutschbein, C. & Futter, M. N. Effect of Climate Change on Soil Temperature in Swedish Boreal Forests. PLoS ONE 9, e93957 (2014).
Qian, B., Gregorich, E. G., Gameda, S., Hopkins, D. W. & Wang, X. L. Observed soil temperature trends associated with climate change in Canada. Journal of Geophysical Research: Atmospheres 116 (2011).
Gavito, M. E., Curtis, P. S., Mikkelsen, T. N. & Jakobsen, I. Interactive effects of soil temperature, atmospheric carbon dioxide and soil N on root development, biomass and nutrient uptake of winter wheat during vegetative growth. J Exp Bot 52, 1913–1923 (2001).
De Kauwe, M. G. et al. Forest water use and water use efficiency at elevated CO2: a model-data intercomparison at two contrasting temperate forest FACE sites. Glob Change Biol 19, 1759–1779 (2013).
Schwalm, C. et al. Sensitivity of inferred climate model skill to evaluation decisions: a case study using CMIP5 evapotranspiration. Environmental Research Letters 8, https://doi.org/10.1088/1748-9326/8/2/024028 (2013).
Schwalm, C. et al. Toward “optima” integration of terrestrial biosphere model. Geophysical Research Letters 42, https://doi.org/10.1002/2015GL064002 (2015).
Wei, Y. et al. The North American Carbon Program Multi-scale Synthesis and Terrestrial Model Intercomparison Project – Part 2: Environmental driver data. Geosci. Model Dev. 7, 2875–2893 (2014).
Kendall, M. A., & Stuart, A. The advanced theory of statistics. 2nd ed. Londres: Charles Griffin (1967).
Mann, H. B. Nonparametric Tests Against Trend. Econometrica 13, 245–259 (1945).
Yue, S., Pilon, P., Phinney, B. & Cavadias, G. The influence of autocorrelation on the ability to detect trend in hydrological series. Hydrol. Process. 16, 1807–1829 (2002).
Blain, G. C. The Mann-Kendall test: the need to consider the interaction between serial correlation and trend. Acta Scientiarum. Agronomy 35, 393–402 (2013).
Yue, S. & Hashino, M. Long term trends of annual and monthly precipitation in Japan. J. Am. Water Resour. Assoc. 39, 587–596 (2003).
Funding for the Multi-scale synthesis and Terrestrial Model Intercomparison Project (MsTMIP; http://nacp.ornl.gov/MsTMIP.shtml) activity was provided through NASA ROSES Grant #NNX10AG01A. Data management support for preparing, documenting, and distributing model driver and output data was performed by the Modeling and Synthesis Thematic Data Center at Oak Ridge National Laboratory (ORNL; http://nacp.ornl.gov), with funding through NASA ROSES Grant #NNH10AN681. Finalized MsTMIP data products are archived at the ORNL DAAC (http://daac.ornl.gov). JBF carried out the research at the Jet Propulsion Laboratory, California Institute of Technology, under a contract with the National Aeronautics and Space Administration. California Institute of Technology. Government sponsorship acknowledged. JBF was supported in part by NASA’s CARBON program. Copyright 2019. All rights reserved. Changhui Peng acknowledges the support by National Science and Engineering Research Council of Canada (NSERC) discovery grant.
The authors declare no competing interests.
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El Masri, B., Schwalm, C., Huntzinger, D.N. et al. Carbon and Water Use Efficiencies: A Comparative Analysis of Ten Terrestrial Ecosystem Models under Changing Climate. Sci Rep 9, 14680 (2019). https://doi.org/10.1038/s41598-019-50808-7
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