The biogeophysical effects of idealized land cover and land management changes in Earth system models
Land cover and land management change (LCLMC) has been highlighted for its critical role in mitigation scenarios, both in terms of global mitigation and local adaptation. Yet, the climate effect of individual LCLMC options, their dependence on the background climate and the local vs. non-local responses are still poorly understood across different Earth system models (ESMs). Here we simulate the climatic effects of LCLMC using three state-of-the-art ESMs, including the Community Earth System Model (CESM), the Max Planck Institute for Meteorology Earth System Model (MPI-ESM) and the European Consortium Earth System Model (EC-EARTH). We assess the LCLMC effects using the following four idealized experiments: (i) a fully afforested world, (ii) a world fully covered by cropland, (ii) a fully afforested world with extensive wood harvesting and (iv) a full-cropland world with extensive irrigation. In these idealized sensitivity experiments, performed under present-day climate conditions, the effects of the different LCLMC strategies represent an upper bound for the potential of global mitigation and local adaptation. To disentangle the local and non-local effects from the LCLMC, a checkerboard-like LCLMC perturbation, i.e. alternating grid boxes with and without LCLMC, is applied. The local effects of deforestation on surface temperature are largely consistent across the ESMs and the observations, with a cooling in boreal latitudes and a warming in the tropics. However, the energy balance components driving the change in surface temperature show less consistency across the ESMs and the observations. Additionally, some biases exist in specific ESMs, such as a strong albedo response in CESM mid-latitudes and a soil-thawing-driven warming in boreal latitudes in EC-EARTH. The non-local effects on surface temperature are broadly consistent across ESMs for afforestation, though larger model uncertainty exists for cropland expansion. Irrigation clearly induces a cooling effect; however, the ESMs disagree whether these are mainly local or non-local effects. Wood harvesting is found to have no discernible biogeophysical effects on climate. Overall, our results underline the potential of ensemble simulations to inform decision making regarding future climate consequences of land-based mitigation and adaptation strategies.
Land cover change and land management change have been intrinsically connected to human development throughout history. The impact of land cover change and land management change (LCLMC) on the global carbon cycle was estimated at 116 PgC based on global compilations of carbon stocks for soils (Sanderman et al., 2017), and for vegetation, it was estimated as 447 PgC (Erb et al., 2018), constituting a loss of about half of the world's terrestrial biomass, with substantial shares already in the pre-industrial period (Canadell et al., 2021). About 10 % of anthropogenic CO2 emissions have been caused by LCLMC over the last decade (Friedlingstein et al., 2022). According to integrated assessment models, LCLMC will play an important role in the near-term future, as most low-end warming scenarios assume large-scale deployment of land-based mitigation (IPCC, 2018). However, the effect of changed land cover and management on the climate is still highly uncertain and poorly understood (Mahmood et al., 2014; Pitman et al., 2009; Perugini et al., 2017). For instance, land use policies generally only account for the effects on the carbon balance while largely neglecting the biogeophysical effects (Duveiller et al., 2020). These biogeophysical effects include (i) the effects of land cover and land management change on the surface radiation budget (e.g. a forest is a darker surface than open grass or cropland; hence, it absorbs more shortwave radiation); (ii) the effects of non-radiative processes like changes in evaporative efficiency and surface roughness; and (iii) the effects induced by atmospheric circulation through altering heat, moisture and momentum transport (Bright et al., 2017; Winckler et al., 2017; Duveiller et al., 2020). The induced changes in atmospheric circulation are often classified as non-local processes, as they typically affect other regions besides those where the LCLMC occurred. The effects on surface radiation and surface properties are called local processes, as they are a direct consequence of local LCLMC.
As LCLMC is an often-cited approach for local mitigation and adaptation policies (Minx et al., 2018; Perugini et al., 2017), the separation of local and non-local effects can help in reducing current uncertainty in assessments of biogeophysical effects. As non-local effects are a consequence of LCLMC occurring elsewhere, they are generally not a desired effect from specific policies (which tend to have a local scope) but are rather an undesired and unintended effect from LCLMC across the globe. In contrast, local effects from LCLMC are directly influenced by local decisions and can be applied more directly in local adaptation and/or mitigation policies. Therefore, the separation between local and non-local effects is beneficial for the implementation of biogeophysical effects related to LCLMC in local mitigation and adaptation policies.
A first set of studies attempted to use Earth system models (ESMs) to understand the global effects of land cover change, both in idealized (Davin and de Noblet-Ducoudre, 2010; Boysen et al., 2020; Meier et al., 2021) and in more realistic setups (Pitman et al., 2009; Pongratz et al., 2010; Boisier et al., 2012; Ito et al., 2020). However, these studies only show the aggregated effects of the biogeophysical processes highlighted above, and no direct separation is made between effects caused by local and non-local processes. Some studies extracted the local signals from Earth system model (ESM) simulations by comparing data at tile level (Malyshev et al., 2015) or extracting local signals by comparing neighbouring grid cells with different land cover change rates (Kumar et al., 2013; Lejeune et al., 2017). Nevertheless, these approaches either have a limited spatial coverage (Kumar et al., 2013; Lejeune et al., 2017) or are limited to ESMs with tile-level output data (Malyshev et al., 2015). A novel approach by Winckler et al. (2017), often referred to as the checkerboard approach, separates land cover change signals into local and non-local effects without these limitations. This was done by prescribing a land cover map with grid cells which underwent land cover change and grid cells with the original land cover in a regular pattern (e.g. , ). By contrasting this simulation to a reference simulation without land cover change, the local and non-local signals can be separated. However, the simulations performed in Winckler et al. (2017) are limited to a single ESM (MPI-ESM, Winckler et al., 2017, 2019a, b, c). Multi-model studies, like the step-wise deforestation experiment within the Land Use Model Intercomparison Project (LUMIP, Boysen et al., 2020), report local and non-local effects by comparing results within and beyond the geographical region of deforestation, which, however, does not allow for a quantitative separation on the global scale.
A second set of studies investigated the climate effects of land cover change based on observational data. Remote sensing data are used to compare the surface temperature of a forested patch and a patch of open land, both spatially (Duveiller et al., 2018; Li et al., 2015) and temporally (Alkama and Cescatti, 2016). Data from eddy covariance towers providing direct flux measurements (e.g. through FLUXNET) were used to reconstruct the biogeophysical effects of deforestation (Bright et al., 2017). These observational estimates by design exclude the non-local signals which might dominate the response to deforestation according to recent work applying the alternating LCLMC approach (Winckler et al., 2019a).
Unlike land cover change, the climate effects of land management change, like irrigation and wood harvesting, are less studied. This is remarkable, as observational studies indicate that both land cover change and land management change have an equally important effect on climate variables such as surface temperature (Luyssaert et al., 2014). Moreover, land management will be increasingly important towards the future due to land scarcity and the need for intensification, as well as the additional pressure on land for carbon dioxide removal (Pongratz et al., 2021). Among land management change options, irrigation has a clear regional cooling effect, especially during warm episodes (Hirsch et al., 2017; Thiery et al., 2017, 2020; Chen and Dirmeyer, 2019; Gormley-Gallagher et al., 2022; Mishra et al., 2020). Despite its recognized imprint on local climate, only a few ESMs simulate irrigation explicitly, with only three ESMs including irrigation in the CMIP6 simulations (Al-Yaari et al., 2022). Wood harvesting has mostly been studied for its biogeochemical effects, while the analysis of the biogeophysical effects is still lacking in studies using ESMs. Observational studies, however, indicate an effect of wood harvesting on albedo (Otto et al., 2014) and surface roughness (Nakai et al., 2008). Furthermore, the effect of land management change on atmospheric circulation has been hypothesized, with, for instance, irrigation-induced cooling causing a delayed onset of the Indian Monsoon (Guimberteau et al., 2012; Thiery et al., 2017) and modified precipitation patterns in eastern Africa (De Vrese et al., 2016). Yet, the relative importance of local versus non-local effects induced by land management changes has not been studied so far.
In this study, we quantify the sensitivity of local and non-local climate to LCLMC and investigate the processes contributing to surface temperature changes. We apply the checkerboard approach to idealized simulations in a multi-model framework using three ESMs. Idealized simulations are performed with two land cover change sensitivity experiments (cropland expansion and afforestation) and two land management change sensitivity experiments (irrigation and wood harvest expansion). The simulations represent changes from present-day land cover and thus provide policy makers with information on the potential effects of LCLMC under the present-day climate. First, we describe the spatial patterns of the local and non-local effects of surface temperature to the LCLMC sensitivity experiments. Second, we evaluate the local effect in the different ESMs of deforestation against estimates derived from observations and remote sensing (Duveiller et al., 2018; Alkama and Cescatti, 2016; Li et al., 2015; Bright et al., 2017). Finally, we analyse the processes underpinning the local effect of different LCLMCs using an energy balance decomposition.
2.1 ESM sensitivity experiments
2.1.1 Participating ESMs
The following three state-of-the-art ESMs are used in this study: the Community Earth System Model (CESM), the Max Planck Institute for Meteorology Earth System Model (MPI-ESM) and the European Consortium Earth System Model (EC-EARTH). Here, we provide a brief technical description of each model.
We use CESM version 2.1.3 (hereafter referred to as CESM), an open-source and fully coupled ESM (Danabasoglu et al., 2020). CESM combines the Community Atmosphere Model version 6 (CAM6), the Community Land Model version 5 (CLM5; Lawrence et al., 2019), the Parallel Ocean Program version 2 (POP2), The Community Ice Sheet Model (CISM), the Los Alamos National Laboratory Sea Ice model (CICE) and the Model for Scale Adaptive River Transport (MOSART). CESM has some notable improvements in comparison to the previous version (Danabasoglu et al., 2020); for instance, CLM5 includes improvements in the snow and plant hydrology, the lake model, and carbon and nutrient recycling (Lawrence et al., 2019). CLM5 also includes 14 natural plant functional types (PFTs) and 8 crop functional type (CFTs), whereby CFTs can exist on either a rainfed patch or an irrigated patch. The sub-grid heterogeneity is implemented using a nested hierarchy where an individual grid cell constitutes different land units such as vegetated, urban, lake, glacier and crop fractions (Lawrence et al., 2019). The CESM simulations were performed at a spatial resolution of .
The Max Planck Institute for Meteorology Earth System Model version 1.2 with a low-resolution configuration (MPI-ESM1.2-LR; hereafter referred to as MPI-ESM) is a fully coupled state-of-the-art ESM that uses the atmospheric component ECHAM6.3 and the land component JSBACH3.2 (around 200 km horizontal resolution (T63) and 47 atmospheric vertical levels), which are coupled via OASIS3-MCT to the ocean dynamic (MPIOM1.6) and ocean biogeochemistry (HAMOCC6) models (around 150 km grid spacing and 40 vertical levels). A detailed description of MPI-ESM1.2 can be found in Mauritsen et al. (2019). A similar setup has been also used within CMIP6 and LUMIP, e.g. with studies on the biogeophysical effects of deforestation (Boysen et al., 2020), as well as other recent studies on the effects of land use and land cover change on climate (Winckler et al., 2019a, b). JSBACH3.2 simulates, in total, 12 different plant functional types (PFTs), with 4 forest PFTs (tropical broadleaf evergreen and deciduous trees, extra-tropical evergreen and deciduous trees) and 2 cropland PFTs (C3 and C4 crops). The MPI-ESM simulations were performed at a spatial resolution of .
EC-EARTH is a state-of-the-art Earth system model developed by the EC-Earth consortium (Döscher et al., 2022). In this study we use the released version EC-Earth3-Veg (v220.127.116.11). The atmospheric component is the Integrated Forecast System (IFS) that was developed by the European Centre for Medium Range Weather Forecasts (ECMWF) and uses the TL255 horizontal grid (± 80 km) and 91 vertical model levels, with the top level at 0.01 hPa. The oceanic component is the Nucleus for European Modelling of the Ocean (NEMO) model (v3.6). The vegetation model is the Lund–Potsdam–Jena General Ecosystem Simulator (LPJ-GUESS). Note that this is a dynamic vegetation model which does not explicitly solve the energy balance as the previous ESMs did. The atmosphere model IFS has a dedicated land surface component, namely the Hydrology Tiled ECMWF Scheme for Surface Exchanges over Land (HTESSEL), to handle the surface water and energy fluxes to the atmosphere. In LPJ-GUESS, the vegetation dynamics for the land are simulated on six stand types, namely natural, pasture, urban, crop, irrigated crop and peatland. In the natural stand, 10 woody and 2 herbaceous PFTs compete (Smith et al., 2014). On pasture, urban and peatland fractions, two herbaceous species are simulated, conforming to the C3 and C4 photosynthetic pathways. The crop stands have five CFTs, both annual and perennial C3 and C4 crops and C3 N fixers (Lindeskog et al., 2013). The EC-EARTH simulations were performed at a spatial resolution of .
There are some important differences in how the different ESMs treat land cover. They have a different amount of PFTs, which are also defined in different categories. Moreover, while in MPI-ESM and CESM land cover is handled within one single sub-model (their respective land surface schemes JSBACH and CLM) and is prescribed, in EC-EARTH there are different models for vegetation dynamics and biogeochemistry (LPJ-GUESS) and for the water and energy cycle (HTESSEL). We summarize the most important differences relating to how the ESMs handle land cover in Table 1. Additionally, in order to give an idea of the differences in the initial land cover maps, we provide the 2015 forest fractions (evergreen, deciduous and total forest) for all ESMs in Appendix A.
2.1.2 Experimental design
We conducted four idealized LCLMC simulations and one reference simulation using the three ESMs. Every simulation has the same set-up but differs in terms of land cover and land management. As we want to remain independent of any future climate scenarios, the simulations will be performed under present-day (2015) climate forcing. They will cover the entire globe so as to inform us where LCLMC might be more or less useful. The following four idealized sensitivity experiments are investigated: (i) a fully afforested world (FRST), (ii) a full-cropland world (CROP), (iii) a fully afforested world with extensive wood harvesting (HARV) and (iv) a full-cropland world with extensive irrigation (IRR). In order to be able to distinguish between the local and non-local effects of these four idealized cases, the LCLMC perturbations are applied following the checkerboard approach of Winckler et al. (2017) using a checkerboard pattern which is detailed in Sect. 2.1.3, effectively meaning that only half of the grid cells undergo LCLMC. In addition, a control simulation with present-day land cover is performed by every ESM to serve as a reference (hereafter referred to as CTL). The CTL simulation uses the native, present-day land cover map of each ESM, which are all based on the Land Use Harmonization version 2 dataset (LUH2; Hurtt et al., 2020). This implies that each ESM retains its native PFTs. The CTL simulation does not include land management (i.e. irrigation and wood harvesting are set to zero) to have a clear baseline for the sensitivity simulations. In all simulations, anthropogenic forcing (including greenhouse gas and aerosol concentrations) is kept constant at the 2015 conditions. The initial conditions are provided by the CMIP6 historical simulations in 2014 and are applied to the different ESMs to conduct model simulations for a period of 160 years. The first 10 years are considered to be a biogeophysical spin-up and are omitted in the analysis. We let the stratospheric aerosols evolve transiently until 2025 based on data from the Scenario Model Intercomparison Project (ScenarioMIP), after which they are kept constant. This was done to ensure that the stratospheric aerosol concentrations in our simulations resemble the mean state of the 21st century. Due to technical constraints in CESM, however, the 2025 levels were used from the start of the simulation. The solar forcing is kept at natural oscillations, except in the case of CESM, where these are set to a constant value that is chosen to be equal to the average over the entire simulation period. This is needed to ensure that all ESMs have the same amount of solar energy entering the system over the entire simulation period. Overall, the set-up is designed to represent present-day climatic conditions through model simulations that are sufficiently long to average out internal variability. All simulations are performed in a fully coupled mode, consistent with the LUMIP protocol (Lawrence et al., 2016), and at each ESM's typical spatial resolution employed for CMIP6 (lat × long) (MPI-ESM: , CESM: , EC-EARTH: ).
The different LCLMC scenarios used in the sensitivity experiments are outlined in Table 2. The idealized land cover maps for CESM and MPI-ESM are constructed following the approach described in Davin et al. (2020) using prescribed idealized land cover maps. To create the idealized FRST land cover map, we start from the 2015 land cover map of each model. All PFTs that are neither forest nor bare soil were removed. The remaining forest fractions are increased such that fractions within a grid cell add up to 100 %. As the bare-soil fraction is preserved, the resulting land cover map only contains forest PFTs and bare soil. The approach mimics forest expansion across all vegetated, cropland and urban areas but avoids trees being planted in e.g. desert, high-altitude and tundra regions (Fig. 1d–f). Note that this approach is only possible for grid cells containing forest PFTs. For grid cells without forest PFTs present, we calculate the latitudinal average (at each ESMs native resolution) of the relative forest PFT distribution consisting of different species. This value is then considered to be representative for this latitudinal band and is used to replace all other vegetation in the grid cell. The same approach is followed for constructing the CROP map by keeping the crop fraction constant within a grid cell and removing all non-cropland PFTs (e.g. pasture, bush, forest and grassland; Fig. 1a–c).
In the version of EC-EARTH used in this study, which simulates vegetation dynamically (Döscher et al., 2022), a different strategy was chosen. In order to obtain a simulation close to a 100 % forest world, the managed vegetation is turned off. Consequently, the fully forested world simulation in EC-EARTH can also contain grasses. For the CROP simulation, the natural land cover is switched off, which forces the model to only grow crops within a grid cell. As in the other ESMs, bare-soil fractions were retained, while only vegetated areas and urban areas where considered for land cover change. Note that this difference in the implementation of the LCLMC has led to strong differences in the total extent of the LCLMC, most notably regarding the afforestation experiment where EC-EARTH shows little afforestation in contrast to MPI-ESM and CESM (Fig. 1f). This directly follows from the assumptions embedded within the land surface component of EC-EARTH (LPJ-GUESS). As for CESM and MPI-ESM, the areas which are afforested are assumed to be a physical forest immediately, which is in contrast to EC-EARTH, where the dynamic vegetation model determines the physical properties of trees from biomass buildup through vegetation growth. This leads to the low amounts of afforestation modelled in the EC-EARTH FRST simulation, which makes it that it is less comparable to the other ESMs for this land cover change.
For the IRR simulation, we apply the same land cover maps as in the CROP simulation, but here, the native irrigation parameterization of each model is activated and applied at the global scale (Fig. 1g–i). Although the individual implementations of the irrigation parameterization differ, all models follow a similar logic. Once a crop suffers a certain amount of water stress (defined differently in the models; see Appendix B), this amount is replenished by applying an irrigation flux until the water stress is relieved. In CESM and EC-EARTH, no limit is imposed on water available for irrigation. In MPI-ESM, however, water availability is limited by the amount of runoff and drainage in the grid cell.
The amount of wood harvesting is typically a prescribed value in ESMs, often expressed as an amount of biomass carbon extracted from the PFTs. In the HARV simulation, we force the models to use the wood harvest rates specified in the CMIP6 SSP5-8.5 scenario by the end of the century (Fig. 1j–k). We let the forest grow as in the FRST simulation without harvesting for the first 40 years to build up biomass before prescribing the intensive wood harvest rates. For the remaining 120 years of the simulation, the harvest rates are kept constant. It should be noted that EC-EARTH did not provide this simulation. In MPI-ESM, there is no feedback implemented for this management practice to any atmospheric processes. Therefore, only CESM can be used to investigate the biogeophysical effects due to wood harvesting.
The idealized sensitivity experiments are conducted under present-day climate forcing. The effects of the different LCLMC strategies represent an upper bound on the potential for global mitigation and local adaptation against the current background climate. They should therefore not be perceived as realistic futures. Both CESM and MPI-ESM show extreme land cover changes in the CROP and FRST simulations compared to CTL (Fig. 1a–f). Overall, the land cover change is stronger in CESM than in MPI-ESM, but the spatial patterns roughly match. Some notable differences include the extent of cropland expansion in Siberia and the amount of afforestation in Australia. Do note that in panels (a) and (b), the amount of cropland expansion (i.e. all conversions to crop) shown is not equivalent to the amount of deforestation (i.e. all conversion from forest to crop) in these simulations, as other conversions (e.g. bush and grassland to crop) also occur.
The comparison of land management between CESM and MPI-ESM shows strong differences despite using a qualitatively consistent implementation across both ESMs. For wood harvesting, the spatial pattern and intensity differ notably. In CESM, the wood harvesting is generally more intense locally and less homogeneous across space than in MPI-ESM (Fig. 1j–k). For irrigation, the spatial extent also differs strongly between the models. Most notably, due to the simple irrigation scheme implemented in MPI-ESM (see Appendix B), this model shows high irrigation amounts in the boreal latitudes, while no irrigation occurs in CESM and EC-EARTH at these latitudes (Fig. 1g–i). Note that, within EC-EARTH, irrigation is implemented in the dynamic vegetation model LPJ-GUESS but not within the atmosphere model IFS (due to both models having a separate water cycle). Therefore, climate effects within this ESM from irrigation expansion can only occur due to increased vegetation growth as a consequence of the ample water availability (Döscher et al., 2022).
2.1.3 Extraction of local and non-local signals
To disentangle the local and non-local effects due to LCLMC, the checkerboard approach of Winckler et al. (2017) is applied and is described here briefly (see Winckler et al., 2017, for details). The checkerboard approach alternates LCLMC grid cells with grid cells which remain unaltered. This allows for a clean separation of local and non-local effects, as the latter only occur over unaltered grid cells, while the grid cells where LCLMC did occur represent a combination of both local and non-local effects. In our simulations, one out of two grid cells are affected by the LCLMC, and these cells are spread out in a regular checkerboard pattern. The checkerboard-like LCLMC alternation is applied to all simulations except the CTL simulation. This means that, for each simulation, only half of the grid cells undergo LCLMC. The remaining unchanged grid cells show the exact same land cover as the CTL simulation. The 150-year simulation is split into five slices of 30 years each. To account for natural variability, we treat each slice as a member of a perturbed-initial-condition ensemble. A multi-year monthly mean is computed over each of these ensemble members. To extract the local and non-local signals, we subtract a land cover change member (CROP or FRST) from its corresponding CTL member. The resulting signals for grid cells where no land cover change occurred cannot be ascribed to any direct (i.e. local) land cover change effect and can therefore be ascribed entirely to non-local effects caused by LCLMC in other grid cells. We then spatially interpolate (using linear interpolation) these values to get a global map of non-local effects. The differences between both ensemble members for grid cells where land cover change did occur are caused by both local and non-local effects (local effects stem from the land cover change within the grid cell, while non-local effects are caused by land cover change in other grid cells). Hence, these non-local effects are subtracted from the total combined effect to get a local signal. As this local signal can only be calculated over the grid cells where land cover change occurred, we again spatially interpolate this pattern to get a full global map. Finally, the local and non-local signals are summed up to derive the total signal, which corresponds to the signal from an idealized global experiment without the checkerboard-like LCLMC pattern applied. The checkerboard approach is implemented for each model grid at its native resolution. Hence, grid cell sizes vary across the different ESMs. As we have five ensemble members of 30 years for each simulation, we can extract local and non-local signals for each ensemble member, which are then used as a measure of uncertainty coming from natural variability.
The procedure described above can be extended to land management change by using one of the land cover change simulations as a reference simulation instead of the CTL simulation. To extract the signal from irrigation expansion, the IRR simulation is compared against the CROP simulation. In the case of wood harvesting, the HARV simulation is compared to the FRST simulation.
2.2 Evaluation of local signal to deforestation
The modelled responses induced by deforestation are evaluated against products from observational studies. Several studies provide global estimates of the effect of deforestation with remote sensing products (Li et al., 2015; Alkama and Cescatti, 2016; Duveiller et al., 2018) or ground observations (FLUXNET; Bright et al., 2017). Only the local signals can be compared here, as these observations only capture local effects by design (Winckler et al., 2019b). All four observational studies represent an idealized case where a fully deforested patch of land is compared to a fully forested patch. We therefore use the local signals derived from comparing the CROP to the FRST simulation to evaluate the ESM response to deforestation against these products. It was shown by Winckler et al. (2019b, c) that a comparison between modelled response and these observational estimates is useful to evaluate the performance of ESMs in representing the effects of LCLMC on surface temperature.Duveiller et al. (2018, 2020)Duveiller et al. (2021)Li et al. (2015)Alkama and Cescatti (2016)Bright et al. (2017)
a These data were first published in 2018 but were later extended to cover a larger area in 2020; as the extended dataset is used in this study, we will refer to this dataset as DV20 from hereon. b Note that the sensible heat flux was obtained by the closure of the energy balance.
The evaluation is also performed for several other variables of interest, including latent heat flux, sensible heat flux, albedo and near-surface air temperature (2 m temperature, tas in CMIP6 nomenclature); however, not all of these are available in each dataset (see Table 3). The spatial extent of the observational studies varies strongly; therefore, the evaluation will be performed along latitudinal bands following Meier et al. (2018) to focus on the global patterns. A description of the different observational datasets used and their spatial maps are provided in Appendix C.
2.3 Energy balance decomposition for changes in surface temperature
An energy balance decomposition approach is used to decompose the change in surface temperature to its driving surface processes. Here, we use this approach to understand the processes underlying the modelled effects of LCLMC. We use the approach developed by Juang et al. (2007) and modified by Luyssaert et al. (2014), which has often been used in LCLMC studies, notably with CLM (Akkermans et al., 2014; Hirsch et al., 2018; Thiery et al., 2017; Hauser et al., 2019; Vanderkelen et al., 2021). The energy balance equation is as follows:
where ϵ is the surface emissivity, σ is the Stefan–Boltzmann constant W m−2 K−4, Ts is the radiative surface temperature as it is directly calculated from surface upwelling longwave radiation, α is the surface albedo, and SWin and LWin are the incoming shortwave and incoming longwave solar radiation, respectively. LHF and SHF are the latent and sensible heat flux, respectively. All fluxes are expressed in W m−2. We take the total derivative to obtain the change in surface temperature, whereby ϵ can be assumed to be equal to 1 for the application of this equation (Juang et al., 2007; Luyssaert et al., 2014).
Here, we apply the energy balance decomposition only to the local effects derived from the LCLMC signals, as these are directly linked to changes in surface properties (Winckler et al., 2017). While applying this approach, a modest global imbalance of less than 0.1 W m−2 is found over all land grid cells for all different cases, indicating the general applicability of the method.
3.1 Evaluation of biogeophysical response to deforestation
We compare observational estimates to the simulated local response of full deforestation (CROP–FRST, i.e. the idealized effect of going from a fully forested to a full-cropland world) in order to evaluate the modelled response to deforestation of the different ESMs. The latitudinal responses of the average annual local surface temperature for all ESMs are generally within the observational range (Fig. 2). The latitudinal change in surface temperature is similar to the observational estimates; specifically, there is a warming in the tropics (up to 3 K) and a cooling in the Northern Hemisphere (NH) boreal latitudes (up to −1 K). Only EC-EARTH deviates from this, as it shows no cooling in NH boreal latitudes (50–80∘ N) and even shows a warming. CESM simulates a different sign compared to observations in the NH mid-latitudes (30–50∘ N) but performs reasonably well at boreal latitudes. Overall, MPI-ESM matches reasonably well to the observational estimates. In the tropics, MPI-ESM simulates values near the lower bound of the observational range (0.6 K), while CESM and EC-EARTH simulate values near the upper bound (3 K). In general, all models show a reasonable agreement with the observations, both in sign and magnitude over most latitudes; only in the NH mid-latitudes and boreal latitudes did the models diverge from the observed range.
Comparing the local effect of deforestation on surface temperature across seasons generally shows a good agreement of MPI-ESM with the observational estimates for the different seasons (Fig. 3). The CESM simulations lie within the observational range for boreal winter and fall but show a cooling response to deforestation in boreal spring and summer above 30∘ N, which is in contrast to the observed warming. The EC-EARTH simulations agree well with the observations, except in the case of the boreal latitudes, where a sustained warming occurs over all seasons except during the boreal summer.
The effect of deforestation on annual local latent and sensible heat fluxes agrees well with the observational estimates for all ESMs (Fig. 4a, b). The latent heat flux is modelled to decrease over most latitudes. MPI-ESM underestimates the magnitude of the latent heat flux signal over most of the subtropics and shows an overestimation over the boreal latitudes. CESM and EC-EARTH match well to the observations, except at the mid-latitudes, where both ESMs underestimate the decrease in latent heat flux. EC-EARTH shows no change in latent heat flux, except over the tropics, where a clear decrease is shown.
Observations show a deforestation-induced decrease in sensible heat flux in the extra-tropics, a slight increase around 20∘ N and 20∘ S, and a decrease around the Equator. CESM captures the response in sensible heat flux well in the NH but overestimates it in the tropics and projects an opposite sign over most of the Southern Hemisphere (SH). MPI-ESM underestimates the change over most of the latitudes and shows an increase instead of a decrease at boreal latitudes. Similarly to the latent heat flux, EC-EARTH only shows a non-zero effect over the tropics, where the model suggests a strong increase. These strong biases in terms of both latent and sensible heat fluxes in MPI-ESM and EC-EARTH do not appear to affect the surface temperature responses. This could partially be explained by the opposite signs in the biases of both turbulent heat fluxes, which cancel each other out, as is likely the case over boreal latitudes for MPI-ESM and in the tropics for EC-EARTH.
The deforestation-induced albedo change is especially important at boreal latitudes, where it dominates the overall surface temperature response (Davin and de Noblet-Ducoudre, 2010). CESM captures the observed albedo response well, except north of 40∘ N, where it overestimates the albedo change, and south of 30∘S, where it underestimates the albedo change (Fig. 4c). MPI-ESM shows a similar bias in the SH. It also overestimates the brightening in the tropics and boreal latitudes following deforestation and underestimates the brightening over most mid-latitudes.
The bias in albedo response north of 40∘ N could be caused by a strong snow-masking response in both ESMs, as a snow-covered forest is darker than a snow-covered cropland. This would also explain the strong cooling in the boreal spring and summer seasons in CESM (Fig. 3b, c) and the bias in annual surface temperature over the mid-latitudes (Fig. 2). In EC-EARTH, the local albedo change is zero (Fig. 4c); however, there is a stronger non-local albedo change (Fig. D1), which is non-zero over boreal latitudes (Fig. D2). The difference in local albedo effect could be caused by the differences in the simulation set-up for EC-EARTH, where the forest needs to establish throughout the simulation (e.g., biomass and specific land surface properties such as vegetation roughness length, leaf area index and albedo) under the local environmental conditions, while in CESM and MPI-ESM, some of the specific land surface parameters are immediately established at the start of the simulation. This albedo bias due to differences in the simulation set-up likely explains the lack of cooling in boreal latitudes in EC-EARTH (Fig. 3). The results for CESM are in contrast to Meier et al. (2018), who showed that the previous version of CLM (CLM4.5) could reproduce the observed albedo relatively well. However, the differences between our results might be due to differences in the model set-up, as CLM was evaluated in offline mode in Meier et al. (2018) in contrast to the coupled simulations performed here.
The near-surface air temperature is often a preferred metric compared to the surface temperature, as it is more relevant for understanding the perceived temperature and is considered in most policy-relevant metrics, including those used to measure global warming (Arias et al., 2021). For local near-surface air temperature change, CESM and EC-EARTH show a response of similar sign to the observations in the SH and tropics. The observations diverge north of 40∘ N, where the DV20 dataset confirms the cooling which is simulated by CESM and MPI-ESM. In contrast, the AL16 dataset shows no temperature change, which is also the case for EC-EARTH (Fig. 4d). The near-surface air temperature in MPI-ESM is relatively insensitive to deforestation, except north of 40∘ N, as was also shown in Winckler et al. (2019c). However, it should be considered that near-surface air temperature is a highly contested measure, as its definition tends to vary strongly across different ESMs, especially over grid cells or grid cell fractions covered with tall vegetation (Boysen et al., 2020; Winckler et al., 2019c). Therefore, in the remainder of this study, we will focus on the response of LCLMC in relation to surface temperature, while the maps for near-surface air temperature are added in Appendix D for reference.
3.2 Local and non-local effects of LCLMC on surface temperature
This section provides an overview of the signal-separated effects on surface temperature of the different LCLMCs across the different ESMs. We discuss the local, non-local and total effects per LCLMC category. At the end of the section, the changes which are consistent across all ESMs are summarized in Table 4.
3.2.1 Cropland expansion
As a consequence of cropland expansion (CROP–CTL), CESM shows a strong local cooling over the NH boreal latitudes which extends into most of the NH mid-latitudes (Fig. 5a). The tropics and subtropics show a strong local warming of up to 4 K over the (deforested) tropical rainforests. MPI-ESM shows a similar pattern to CESM in NH boreal latitudes but with a smaller local cooling which does not extend as far south into the NH mid-latitudes. MPI-ESM also simulates local warming over the tropics but with a different spatial pattern and magnitude compared to CESM and EC-EARTH. The local signals in EC-EARTH are similar to CESM, showing a strong local warming in the tropics. However, in NH boreal latitudes, the signals are mixed, with a cooling over the (deforested) boreal forests and a strong warming over the permafrost-covered areas (Siberia, northern Canada and Alaska). This NH boreal warming is most likely due to the shift in the EC-EARTH simulation from natural land to managed land, leading to a shorter duration of frozen soils throughout the year, which causes a soil warming.
In CESM, the local cooling is amplified by a strong non-local cooling over these regions. The non-local effect in MPI-ESM strongly differs from CESM. While CESM simulates a widespread cooling, MPI-ESM shows a weaker but clear warming over the boreal regions, Europe and the eastern USA. The non-local effect in EC-EARTH is mixed, with a warming over the Arctic regions and the Sahara and a cooling in the mid-latitudes and tropics. In all ESMs, the local signals dominate the total response in the tropics. The non-local effect also dominates over NH boreal latitudes in CESM and MPI-ESM, while in EC-EARTH, the pattern differs regionally.
In the afforestation sensitivity experiment (FRST–CTL), the local response is similar to the response in the cropland expansion sensitivity experiment but shows an opposite sign, as expected (Fig. 6). A local cooling is simulated over the tropics for all ESMs, and a local warming is simulated over the boreal latitudes for both MPI-ESM and CESM. The shift from cooling to warming occurs at a higher latitude in MPI-ESM and EC-EARTH compared to in CESM. The lack of local boreal warming in EC-EARTH is probably related to the differences in experimental set-up and the resulting low amounts of afforestation in this simulation (Fig. 1f). The non-local effects due to afforestation result in warming for all ESMs, except over the North Atlantic in CESM. This indicates that the non-local effect is dominated by the albedo decrease, which originates from the strong snow-masking effect of forest compared to open cropland. This is also indicated by the fact that the non-local warming dominates over the extratropics for all ESMs in contrast to the local cooling which dominates over the tropics and parts of the subtropics (depending on the ESM).
In CESM, this albedo-induced warming causes a cooling blob in the North Atlantic (Fig. 6b). A similar but opposite pattern is also apparent in the cropland expansion experiment with CESM (Fig. 5b), but this appears as a warming blob with a lower magnitude. The same warming blob was also found in the LUMIP deforest-glob experiments by Boysen et al. (2020). A plausible explanation for this dynamic is the different latitudinal effect of the LCLMC option. With a high-latitude hemispheric warming and a slight cooling in low latitudes, the thermodynamic response of the Atlantic meridional overturning circulation (AMOC) would indicate a weakening due to a decrease in the temperature gradient, similarly to thermodynamically driven AMOC weakening due to arctic amplification under climate change scenarios (Schleussner et al., 2014). Inversely, global-scale cropland expansion causes non-local cooling, except for a localized warming over the North Atlantic. It should be noted, however, that this strong North Atlantic response in CESM is not consistent throughout the entire simulation period despite its high magnitude. The global non-local warming pattern has large implications for future deployment of land-based mitigation strategies, especially for boreal afforestation. However, it should be noted that non-local signals are highly dependent on the spatial pattern, as well as the extent of the prescribed land cover change (Winckler et al., 2019a)
3.2.3 Irrigation expansion
In the idealized irrigation expansion sensitivity experiment (IRR–CROP, i.e. irrigation expansion in a full-cropland world), both MPI-ESM and CESM agree on the irrigation-induced reduction in local surface temperature, while irrigation expansion in EC-EARTH does not induce any local effects (Fig. 7). The very limited local effects in EC-EARTH are caused by a lack of moisture exchange between IFS and LPJ-GUESS, whereby water added in LPJ-GUESS for irrigation does not affect the moisture fluxes in IFS. Hence, in EC-EARTH, irrigation affects crop growth and albedo but does not alter turbulent surface fluxes. In MPI-ESM and CESM, temperature decreases globally due to irrigation expansion, but there are substantial differences in the spatial patterns between the models. These differences partially stem from the large differences in the irrigation amounts imposed in the different models (Fig. 1i–k). EC-EARTH shows some non-local temperature effects, but these are small in magnitude, and the sign differs across different regions. In CESM, the total signal is dominated by the local response, with only a modest contribution of non-local effects. The non-local irrigation signal in MPI-ESM is generally stronger than the local signal and dominates the total response.
These results corroborate the findings of Thiery et al. (2017) and Chen and Dirmeyer (2019), who found that irrigation has a cooling potential due to an increased latent heat flux over irrigated areas. CESM simulates strong local cooling effects in the subtropics and tropics, while MPI-ESM shows the strongest local cooling in the NH mid-latitudes and less-apparent local cooling in the tropics. In CESM, there is a non-local irrigation-induced cooling over the NH mid-latitudes, where the local effects are generally small. This indicates that, in these latitudes, a non-local effect, plausibly due to an increase in cloud cover, dominates the effects of irrigation rather than surface processes like evaporative cooling, which dominate the local effects over the tropics. For MPI-ESM, a strong increase in cloud cover appears to cause the strong non-local cooling (Fig. E15).
3.2.4 Wood harvest expansion
The effect of wood harvesting (HARV–FRST) appears to be very small (Fig. 8). There is generally no local effect, and the non-local signal is, overall, weak and inconsistent in sign across the CESM simulation. The simulated non-local signals may well stem from internal climate variability rather than an actual response to land management change. These results imply that the biogeophysical effects of wood harvesting, as simulated here, are too weak to have a significant imprint on global and local climate conditions at the grid scale in the represented ESMs. This does not imply that the biogeophysical effects cannot play a role locally but simply suggests that these effects are not strong enough to be discerned at the currently used grid-scale level and with the process detail of current ESMs. An analysis comparing the simulation results at the tile level (within a grid cell) would provide an alternative approach to analyse possible local effects due to wood harvesting.
3.3 Energy balance decomposition of the surface temperature changes
3.3.1 Cropland expansion
Using Eq. (2), the different factors contributing to the response in surface temperature are assessed when aggregated zonally (Fig. 9) and seasonally (Fig. 10). In the case of cropland expansion, the warming in the tropics for all ESMs is mostly caused by a strong decrease in latent heat flux, possibly as a consequence of a decreased evaporation capacity (Fig. 9a and b). The simulated decrease in sensible heat flux in MPI-ESM reduces the heat transport away from the surface, therefore amplifying the warming, while in CESM, an increase in sensible heat contributes to a cooling. In MPI-ESM, the tropical warming is slightly offset by an albedo increase. In all ESMs, local changes in shortwave and longwave radiation increase the warming signal; however, in EC-EARTH the contribution from enhanced incoming longwave radiation is especially strong, which could indicate that atmospheric properties such as high cloud cover or atmospheric moisture have a strong influence on surface temperature in this model. In CESM, over boreal latitudes, the increase in albedo dominates the surface temperature response, causing a local cooling which is partly offset by a warming induced by a decrease in sensible heat flux. In MPI-ESM, this boreal albedo effect is much weaker, causing no clear local cooling.
In EC-EARTH, the energy balance components do not explain the simulated warming over boreal latitudes, which is most likely related to the fact that EC-EARTH uses the temperature of the first whole soil layer as the surface temperature. As a consequence, other processes that are not related to the surface energy balance (e.g. permafrost thawing) also affect the surface temperature in this model. Finally, contrasting to the other models, the albedo in EC-EARTH does not influence the local surface temperature changes, as there is no change in local albedo (see Fig. E2).
The cooling effect of albedo due to cropland expansion has a pronounced seasonal response in both MPI-ESM and CESM (Fig. 10a and b). It is most outspoken during NH spring as a consequence of the reduced snow-masking effect. In both MPI-ESM and CESM, the latent heat flux has a strong contribution throughout the year. It shows a seasonality which is most pronounced in CESM, peaking in early spring and fall. The sensible heat flux has a warming effect in CESM throughout most of the year, except during the NH fall, when it shows a cooling effect. In EC-EARTH, the sign of all changes is constant throughout the year. There is a slight seasonal effect for the magnitude of the turbulent heat fluxes and longwave incoming radiation, being largest in NH summer and lowest in NH winter. Overall, all ESMs simulate a global surface warming of about 0.3 K due to the local effect of cropland expansion over the year and show a minimal warming in the NH winter.
In the case of afforestation, all models show a reduction of the surface temperature in the SH and tropics (Fig. 9d, e, f). In MPI-ESM and CESM, this is caused by the cooling effect of increasing turbulent heat fluxes, which is partly counteracted by a warming effect due to an albedo decrease. This albedo effect becomes dominant when moving northward and causes a local warming in CESM starting from the mid-latitudes and in MPI-ESM starting from the boreal latitudes. In EC-EARTH, the cooling is caused by changes in sensible heat flux and incoming longwave radiation but is counteracted by a decrease in latent heat flux. At boreal latitudes, the albedo-induced warming is partly counteracted by an increase in sensible heat flux in CESM and by an increase in latent heat flux and a decrease in incoming shortwave radiation in MPI-ESM. The decrease in incoming shortwave radiation might be caused by an afforestation-induced local increase in cloud cover (as shown in Fig. E10). This would be in line with the theoretical understanding that an increase in latent heat flux causes an increase in low cumuliform clouds (Ban-Weiss et al., 2011). Recent observational results show an afforestation-induced cooling effect related to increased cloud cover (Teuling et al., 2017; Duveiller et al., 2021). However, neither CESM nor EC-EARTH represent this increase in cloud cover, with CESM even showing a slight decrease in cloudiness over boreal latitudes (Fig. E10).
The albedo-induced effect of afforestation has a clear seasonal peak during NH spring for both MPI-ESM and CESM (Fig. 10c and d). The turbulent heat fluxes seem to follow a similar seasonality. This indicates that extra-tropical afforestation dominates the global climate response for these models due to a strong albedo response that is largely counteracted by the changes in turbulent heat fluxes. In EC-EARTH, a similar seasonal pattern is visible, with larger fluxes in NH summer and smaller fluxes in NH winter, as was also the case for cropland expansion. Overall, all models show limited local effects due to afforestation, being quasi-0 K in CESM, −0.15 K in MPI-ESM and 0.2 K in EC-EARTH.
3.3.3 Irrigation expansion
For irrigation, only results for MPI-ESM and CESM are shown, as the local surface temperature changes in EC-EARTH are too small for a meaningful decomposition in energy balance components. Both MPI-ESM and CESM show a very different geographic pattern for the irrigation flux (Fig. 1). However, the models appear to be largely consistent when it comes to the identification of the underlying processes causing the change in surface temperature (Fig. 9e and f). The increase in latent heat flux dominates the response. This causes a strong cooling which is counteracted by a strong (but weaker) warming effect caused by the decreased sensible heat flux. Surface albedo increases slightly in CESM, as wet soils are darker. This change contributes to a rise in surface temperature. MPI-ESM, in contrast, shows a slight decrease in albedo, contributing to a lowering of surface temperature. We hypothesize that this albedo decrease in MPI-ESM is a consequence of irrigation causing greener, hence brighter, crops. Longwave and shortwave radiation both give a cooling contribution due to a local increase in cloudiness (Fig. E15).
The seasonal pattern of irrigation is dominated by the application of irrigation during the dry season (Fig. 10e and f). As most land is located in the NH, we find the strongest local cooling during NH spring and summer. This seasonal pattern is stronger in MPI-ESM, as irrigated croplands extend more northward than in CESM (Fig. 1g, h). Globally, both models predict a slight global cooling effect of around 0.2 K.
4.1 Robust patterns in the local response to LCLMC across ESMs
Our results show clear consistencies across CESM, MPI-ESM and EC-EARTH. All three ESMs are able to simulate a response of average annual surface temperature to full deforestation consistent with observational evidence. There remain some clear biases when comparing the ESMs to observations such as a strong albedo response in CESM in the mid-latitudes and a strong (soil-related) warming response in the high latitudes in EC-EARTH. However, general observed patterns such as local cooling over boreal forests and local warming over tropical forests are well captured by the ESMs. The consistency in surface temperature response across ESMs and observations is in stark contrast to the large spread in signals of the turbulent heat fluxes and albedo, which have been highlighted as some of the main driving processes of local temperature change (Davin and de Noblet-Ducoudre, 2010; Winckler et al., 2019c). The energy balance decomposition for the cropland expansion confirms these model biases, which moreover differ across ESMs. For afforestation and cropland expansion, all ESMs show that the tropical response is mainly caused by a change in turbulent heat fluxes. However, they disagree on how these changes occur. All three ESMs show that local latent heat flux changes determine the surface temperature response in the tropics. However, the role of local sensible heat flux changes differs across ESMs, showing a cooling effect in CESM and EC-EARTH in contrast to MPI-ESM , where it has a warming effect. Over boreal latitudes, the albedo dominates the local effect for both cropland expansion and afforestation in CESM and for afforestation in MPI-ESM. EC-EARTH shows that permafrost thawing (unrelated to land cover change) causes the simulated warming in the cropland expansion experiment. For irrigation expansion, MPI-ESM and CESM consistently show that the increase in latent heat dominates the surface temperature response, causing a local cooling. In the current EC-EARTH set-up, there is no coupling of land surface moisture by water fluxes to the atmosphere as caused by irrigation; hence, the only effect on the climate is due to increased growth of crops and respective changes in physical properties.
Although we have harmonized the land cover and management representation across the different models, strong differences remain, most notably in the implementation of irrigation expansion and afforestation (Fig. 1). This implies that the comparison of the different simulations across ESMs is not perfect, and inconsistencies can be caused by disparity in model structure and by spatial differences and differences in the extent and implementation of the applied LCLMC. As for afforestation, the differences found here were mainly caused by the differences in terms of the implementation of forests in EC-EARTH (where the forest and respective land surface properties change throughout the simulation) compared to in CESM and MPI-ESM, which start off with a physical forest and its land surface properties. The differences regarding land management are a direct consequence of these implementations being fairly recent in the various ESMs. There is no consistency in the implementation approach for land management schemes, such as irrigation expansion across ESMs, as was also the case in the early land cover change inter-comparison projects (De Noblet-Ducoudré et al., 2012). Over the last decade, several improvements have been made regarding land cover change to make the ESMs more consistent – for example, using common datasets (Hurtt et al., 2020) and common simulation protocols like the LUMIP experiments under CMIP6 (Lawrence et al., 2016). The same issues that ESMs faced before for land cover change are now apparent for land management change as well. As more ESMs are implementing land management change (Blyth et al., 2021), it is crucial that common datasets and simulation protocols are set up in order to ensure comparability across the various ESMs.
However, despite these limitations, our results show that there remain similarities in the LCLMC response in the different ESMs, most notably regarding the local effects. A consensus is emerging regarding the local effects of deforestation (afforestation) with a clear cooling (warming) at boreal latitudes and a warming (cooling) in the tropics, as is in line with observational evidence. The cooling potential of irrigation (both local and non-local) is confirmed by both MPI-ESM and CESM. However, more research is needed to understand the full implications of these biogeophysical effects. The cooling effects induced by irrigation might be offset by the increased humidity and, overall, might induce an increase in heat stress (Mishra et al., 2020). The effects on warm and cold extremes remain to be investigated as well but lie beyond the scope of the current study.
Our results highlight the importance of including possible local biogeophysical effects in future land use and land management policies. The current policies underpinning large-scale climate mitigation plans, such as the European Green Deal, are set up to only take into account the biogeochemical effects of LCLMC strategies such as afforestation. The European Green Deal plans (European Commission, 2019) rely heavily on afforestation as a possible negative emission technology to enhance the land sink by planning to plant up to 3 billion trees within the EU. However, beyond the positive consequences of afforestation on carbon storage, its biogeophysical effects should also be considered in order to plan for (or avoid) side-effects for regional temperature induced by local processes (as shown in Fig. 6a, e, i). The local biogeophysical effects imply some positive side-effects over specific regions, such as the tropics and mid-latitudes, especially during the summer season; however, they could also imply some negative side-effects over the boreal latitudes and part of the mid-latitudes during the winter season. These findings are in line with Windisch et al. (2021), who highlight the existence of various trade-offs between local biogeophysical effects and biogeochemical effects depending on the season and region. These results further strengthen the need for the inclusion of local biogeophysical effects next to biogeochemical effects in order to have an accurate idea of the mitigation potential of forests in LCLMC policies.
4.2 Inconsistent non-local effects across ESMs due to idealized cropland expansion
The global non-local cooling in CESM, as shown in Fig. 5, is consistent with the findings of a previous global deforestation simulation using the checkerboard approach performed by Winckler et al. (2019a) with MPI-ESM. However, these results strongly contrast with the non-local response found in MPI-ESM here. Some methodological differences should be noted here: Winckler et al. (2019a) performed a fully idealized deforestation experiment, which is more akin to the CROP–FRST comparison in this study than the results of CROP–CTL shown here. It should be noted that, for full deforestation (i.e. CROP–FRST), all ESMs (including MPI-ESM) predict a non-local cooling (Fig. C3), which is consistent with Winckler et al. (2019a). The effect of a cropland expansion (CROP–CTL) in MPI-ESM, which starts from the present-day forest extent, results in a clear non-local boreal warming. Two possible mechanisms could explain this counter-intuitive discrepancy between the non-local response of MPI-ESM and CESM in CROP–CTL in contrast to their consistent results for CROP–FRST: (i) MPI-ESM shows a weaker albedo effect when compared to CESM (Fig. 5c); and (ii), the MPI-ESM model shows a strong decrease in annual boreal cloud cover (see Fig. E5), which is especially strong in boreal summer (not shown) and could cause an additional warming, possibly offsetting any non-local cooling caused by changes in albedo.
In summary, we can state that the non-local effects due to full deforestation presented here are in line with the literature (Winckler et al., 2019a). However, the non-local effects display a larger uncertainty when it comes to the non-local effects of cropland expansion from present-day conditions (i.e. CROP–CTL as presented here). It should be noted that, due to the strong albedo bias in CESM over NH mid-latitudes (see Fig. 4d) and the crucial role of albedo in determining the non-local effects, it is probable that the strong non-local cooling shown over CESM is an overestimation.
4.3 Non-local biogeophysical response due to land-based mitigation and adaptation
Non-local biogeophysical effects can regionally dominate over local biogeophysical effects. The distinct non-local warming found for afforestation is consistent with the inverse outcome obtained from global deforestation experiments in the literature (Winckler et al., 2019a; Davin and de Noblet-Ducoudre, 2010) and is robust across the different ESMs considered here (Fig. 6b, f, j). However, the strong divergence in outcome from the cropland expansion experiments does show that the albedo effect does not completely control the non-local surface temperature responses. A variety of atmospheric processes affecting the atmospheric moisture balance and large-scale atmospheric dynamics need to be assessed in order to better understand the relevant processes. In CESM, a large-scale land cover change even appears to affect global ocean circulation, as was illustrated by the strong AMOC response within this model. It should be noted that this is not a single-model feature, as similar AMOC anomalies were visible for two other ESMs in the LUMIP deforestation simulations (Boysen et al., 2020). More research is needed to fully understand the processes that cause the non-local biogeophysical effects related to large-scale land cover change shown here.
Irrigation clearly decreases temperature in both CESM and MPI-ESM, constituting another demonstration that deploying irrigation could entail side-benefits for local temperature reduction, especially over agricultural land (Thiery et al., 2017, 2020; Hirsch et al., 2017). These results even suggest that achieving climate benefits could become an objective of irrigation deployment, potentially making it a deliberate adaptation strategy if constraints to its implementation (related, for example, to water availability or socio-economic enabling conditions) can be overcome. However, it remains unclear whether the irrigation-induced cooling is predominantly local (induced by turbulent heat fluxes) or non-local (induced by cloud effects) and what the combined effect is of irrigation-induced changes in temperature and humidity patterns on heat stress. Nevertheless, these results help assess the future climate consequences of irrigation expansion. Irrigation has been projected to increase in the future as a means to increase agricultural productivity (van Maanen et al., 2022; Rosa et al., 2020), but it may also aggravate future water stress (Haddeland et al., 2014). It should be noted that irrigation is implemented in a highly idealized way in these simulations, with two out of three ESMs not being constrained by water limitations. These water limitations should be assessed before irrigation expansion can be considered as a viable adaptation option in any region.
Overall, our results show that future land-based mitigation strategies will need to consider the non-local biogeophysical consequences of LCLMC patterns, as large-scale afforestation is a key strategy in intensive land-based mitigation scenarios (Smith et al., 2015; Humpenöder et al., 2014), especially in those compatible with a 1.5 K world (Roe et al., 2019). In particular, the robust non-local biogeophysical warming as a result of global afforestation presented in this study indicates that future land-based mitigation strategies would lead to an even more extensive unintended warming than the local biogeophysical warming that has been widely reported for boreal regions and the mid-latitudes in winter. More research is needed to bridge the knowledge gaps regarding which regions would be mostly responsible for this non-local warming if afforested and what would be the magnitude of this warming in realistic afforestation scenarios.
4.4 Limitations and outlook
The idealized simulations performed in this study give an overview of the potential biogeophysical effects from LCLMC. We were able to separate local and non-local effects due to the application of a checkerboard like LCLMC perturbation to our idealized land cover maps (Fig. 1). The local effects are only caused by changes that occur within the grid cell. Hence, they represent the most extreme possible outcome of the application of a certain LCLMC within that single grid cell without accounting for other LCLMCs around the globe. In contrast, the non-local signals are a compound response caused by the LCLMC around the globe. These represent an underestimate in magnitude of the non-local effects in a simulation of global LCLMC, as, due to the checkerboard pattern, non-local effects are the consequence of LCLMC applied to only half of the grid cells around the globe. As the non-local effects, by design, also capture all internal climate variability, they are more uncertain than the local effects presented here. To limit the uncertainty related to climate variability as much as possible, the simulations could be repeated within an ensemble set-up. However, such a set-up would require substantial additional computation and storage resources.
Furthermore, it should be noted that the application of the checkerboard approach has some methodological implications, as the resulting local and non-local signals intrinsically contain an interpolation error. Although we tried to minimize this error by using a checkerboard pattern of one out of two grid cells, this error can still reach up to 0.3 K based on previous simulations with MPI-ESM (Winckler et al., 2017). Moreover, the approach has limitations due to the size of a grid cell in the different ESMs. The land cover change needed to get a local effect as presented here remains highly unrealistic (around 100 km). As ESMs are becoming computationally more efficient and as their resolution gets increased, the validity of this assumption could be tested using higher-resolution ESMs.
Some biases exist within the evaluation approach, as the modelled surface temperature does not exactly match the radiative surface temperature measured in the observational estimates. For instance, the satellite measurements have an inherent sampling bias, as they only measure during cloud-free conditions. Also, the different observational estimates have different and often non-overlapping spatial coverage. Nevertheless, these observational studies using a diversity of approaches show a large consistency among themselves and thus can act as a benchmark for the representation of land cover change within ESMs (Winckler et al., 2019a, b).
The results shown within this paper highlight some clear consistencies across the ESMs; however, often, the ESMs tend to show differences as well. For example, more work is needed to improve the representation of irrigation, especially for EC-EARTH and MPI-ESM, as MPI-ESM suffers from unrealistic irrigation amounts, especially in the boreal regions, while underestimating the potential irrigation in the subtropics, such as in India. Furthermore, EC-EARTH is currently not a viable model for a study of the biogeophysical effects of irrigation, as water fluxes from land are not communicated to the atmosphere. This limitation is worth addressing, as the implementation of irrigation in ESMs has been shown to make them more realistic over regions of intense irrigation (Al-Yaari et al., 2022). Regarding land cover change, all ESMs still struggle to replicate observed patterns in energy fluxes (Fig. 4). CESM shows a strong overestimation of the albedo in the intermediate latitudes (30–50∘ N), with clear temperature biases over these regions, an issue which could be considered in future developments of this ESM. The afforestation implemented in EC-EARTH in this study could have been improved and made more comparable to the other ESMs by changing the simulation set-up – for example, by forcing the forest to exist from the start of the simulation (as was done in MPI-ESM and CESM) instead of allowing EC-EARTH to model afforestation in accordance with the default set-up of the dynamic vegetation model LPJ-GUESS.
The simulations presented here are unique, as they combine a multi-model approach with a direct separation of local and non-local effects. Further analyses could investigate the effects of LCLMC beyond the seasonal and mean changes in surface properties, heat fluxes and temperature. These simulations allow us to analyse both the transient response of LCLMC-induced biogeochemical effects and the socioeconomic impact of their biogeophysical effects. The non-local effects presented here can further be analysed to gain a better understanding of the circulation changes induced by the LCLMC. A moisture-tracking analysis could be performed to investigate the effects on global precipitation patterns, as previous studies showed that Amazonian deforestation could induce a drying of the region (Lejeune et al., 2015). The local effects diagnosed from these extreme sensitivity experiments could also be used as training data for less computationally expensive statistical models to emulate biogeophysical effects arising from less-extreme and more-realistic LCLMC scenarios. Overall, we hope that the results of the simulations presented here can help increase the present understanding of LCLMC and build towards a framework that facilitates the inclusion of the biogeophysical effects of LCLMC in future policy frameworks.
In this study, we showed the first results of a new slate of fully coupled ESM simulations within a multi-model framework targeted at analysing the effects of land cover and land management change (LCLMC). We simulate the global biogeophysical response to (i) cropland expansion, (ii) afforestation, (iii) irrigation expansion and (iv) wood harvesting using the Community Earth System Model (CESM), the Max Planck Institute Earth System Model (MPI-ESM) and the European Consortium Earth System Model (EC-EARTH). We apply the checkerboard approach of Winckler et al. (2017) to disentangle the local and non-local biogeophysical effects.
A model evaluation is performed for a global deforestation scenario using the local effects derived from the ESM simulations and several observational estimates. All ESMs agree well with the observed annual mean surface temperature change. CESM, however, overestimates the albedo in boreal and mid-latitudes and persistently locates the transition from local warming to local cooling more south compared to the observations. A soil-induced effect in EC-EARTH causes a warming in boreal latitudes. MPI-ESM and EC-EARTH show strong differences in the representation of the turbulent heat fluxes despite their overall agreement with observed surface temperature changes.
The biogeophysical effects of idealized LCLMC are shown to be important and non-negligible to understanding the overall climate impact of LCLMC. Deforestation causes a local warming in the tropics and a cooling over boreal latitudes for all ESMs. For afforestation, a clear tropical cooling is consistent across ESMs. The non-local effects carry more uncertainty, which may be due to a wider variety of mechanisms at play and due to the strong natural variability intrinsic to atmospheric processes. However, this would require further investigation to be confirmed. All ESMs show a strong non-local warming as a consequence of large-scale afforestation. Irrigation expansion cools the climate both through local and non-local effects, although the contribution of local and non-local effects to this cooling is inconsistent across ESMs. Finally, the effect of extensive wood harvesting is shown to be too small to have a clear imprint on the grid-scale climate.
The driving processes underlying the local surface temperature effects were analysed using an energy balance decomposition technique. The local surface temperature effects of land cover change (both cropland expansion and afforestation) are dominated by the response in turbulent heat fluxes in the tropics. In the case of afforestation, the albedo is the dominant factor in boreal latitudes for MPI-ESM and CESM. This is also the case for the local effects in the cropland expansion experiment for CESM in contrast to the MPI-ESM, where turbulent fluxes dominate in the boreal latitudes. In EC-EARTH, the boreal surface temperature change could not be explained by the energy balance decomposition, as the boreal warming is caused by processes that are not included in the simplified version of the surface energy balance, such as permafrost thawing. Moreover, the strong influence of incoming longwave radiation indicates that atmospheric properties (such as cloud cover and moisture content) are strongly related to local surface temperature changes. Both CESM and MPI-ESM agree that the main local surface temperature response due to irrigation is driven by a strong increase in latent heat flux, which is only partly counteracted by a decrease in sensible heat flux.
Overall, our results confirm that the biogeophysical effects of LCLMC are an important factor to consider in future land-planning strategies, especially as they reveal the robust importance of non-local climate responses in the context of the mitigation potential of land cover change. In the case of large-scale afforestation specifically, the non-local response could lead to global-scale unintended warming, particularly over the boreal and mid-latitude regions.
In Fig. A1, the fractions of deciduous, evergreen and total forest cover are shown for the three ESMs. This is to illustrate the differences in the CTL land cover maps, which stem from a different definition of the natural PFTs in each ESM. Although all ESMs are based on the LUH2 dataset, we can still see that there are clear differences in the types of forest modelled (evergreen or deciduous) but also in the total amount of forest.
The soil moisture of the first (0–0.065 m) and second (0.065–0.319 m) soil layers (out of five) is filled at each time step (20–30 min) to field capacity if the field capacity was not reached and if enough irrigation water is available in storage.
Irrigation water is stored at each time step when the reservoir drops below 0.2 m and is filled up with all available water from (surface) runoff and drainage during that time step.
Irrigation is applied daily at the first time step after 06:00 local time only when the soil moisture over all soil layers containing roots falls below a defined target soil moisture, which is defined in order to match present-day irrigation. If soil moisture falls below the target soil moisture, it is replenished until at the target soil moisture level.
The water needed for applying irrigation is taken from river water storage; however, when this is inadequate to meet water demand, it can also be subtracted from the ocean model; therefore, no real water availability limit is applied within CLM.
Irrigation is only applied when the crop leaf area >0; i.e. this means that crops are only irrigated when they are in their vegetation state (during the growing season).
In LPJ-GUESS, the amount of irrigation is the deficit a crop plant is experiencing. So if a crop needs an additional amount of water, it is added to the top of the soil column.
The water comes from nowhere (i.e. unlimited water source).
The water flux is not communicated to IFS; i.e. irrigation does not affect the surface water fluxes within the atmosphere. The only effect is that an irrigated crop would have a higher leaf area index and cover fraction compared to a non-irrigated crop of the same type.
The comparison of the ESM data and the different observational datasets has some inconsistencies, as was already described before by Winckler et al. (2019a). From Fig. C1, it is apparent that the different datasets do not have the same spatial coverage. Besides this, the calculation of the temperature signal differs across studies. In Alkama and Cescatti (2016), the observed signal is extracted by looking at changes over time, which is in contrast to the other studies, where this was extracted by comparing nearby locations during the same time step. Also, different conversion types are considered; in Li et al. (2015) and Duveiller et al. (2020), a generic forest-to-open-land (both crop and grassland) conversion is considered, while in Bright et al. (2017), only a forest-to-grass conversion is considered. In Alkama and Cescatti (2016), apart from forest-clearing-to-grass and forest-clearing-to-crop conversions, windfall events and fires were also included in the analysis. Each dataset also covers different time periods, although all datasets only include data after the year 2000 (hence representing present-day conditions), and the total durations each estimate is based on are similar. All studies provide an estimate of the response of surface temperature to a full deforestation, except Alkama and Cescatti (2016), where actual deforestation was considered and which had to be converted to a full-deforestation signal by weighting with the deforestation fraction; in order to get robust results, only grid cells where more than 1 % of the actual deforestation had occurred over the analysis period considered were selected. For Bright et al. (2017), only data for conversions from specific forest species were provided. To allow for a consistent comparison to the ESMs, these values had to be weighted using the weights of each forest PFT within the specific ESMs. Therefore, an estimate of the Bright et al. (2017) data was created, representing the different ESMs and their PFT distributions; however, these differed only slightly, so an average was taken over all estimates to be compared across all ESMs.
For the creation of the evaluation plots, the signals from the different datasets were calculated over all grid cells where data were available, as most have a sufficient amount of grid cells in each latitudinal band. Each dataset was retained at its original resolution for the calculation of the latitudinal averages in order to avoid interpolation errors. The observational data could be directly compared to the output from the CROP–FRST signal-separated data, as, in most grid cells, almost a full deforestation occurs, as is shown in Fig. C2. The corresponding maps showing the local, non-local and total surface temperature effects are shown in Fig. C3.
The albedo responses (local, non-local and total) are shown for the CROP–FRST case in Fig. D1. This clearly illustrates a peculiar feature related to the EC-EARTH model; while albedo change is mainly local (as is the case for MPI-ESM and CESM), it is completely non-local for EC-EARTH. The colour bar range was chosen to clearly show all (even small) changes in albedo. It shows that the albedo change has a dominant local component for CESM and a smaller non-local component, MPI-ESM only shows a local contribution with no non-local effect, and EC-EARTH only shows a non-local contribution.
This is further illustrated by Fig. D2, where the latitudinal averages of the local, non-local and total effects are compared to the observational datasets from Duveiller et al. (2020) and Li et al. (2015). This again illustrates what was mentioned above; i.e. there is no local component of albedo change for EC-EARTH, while this is the dominant component for MPI-ESM and CESM. However, it also clearly shows that, even when total effects are considered, EC-EARTH strongly underestimates albedo change compared to the observational datasets. This is especially important in the boreal latitudes, where EC-EARTH does show a slight increase in the NH; however, this effect is still less than half as strong as the observational datasets indicate. Due to the specific simulation set-up used in this study, EC-EARTH is not able to grow sufficient amounts of vegetation to cause a clear local albedo effect; only non-local effects are visible for this ESM. In CESM and MPI-ESM, this issue does not occur, as the land cover change immediately implements a physical forest and the related land surface properties without the need for these to grow. It should be noted that, due to this issue, EC-EARTH has undergone less land cover change in the CROP–FRST case compared to the other ESMs, as the FRST simulation for this ESM showed very little afforestation amounts (see Fig. 1), and these forests are only established to a limited extent, causing smaller biophysical effects on the atmosphere.
CESM is an open-source model which can be freely downloaded here (https://www.cesm.ucar.edu/models/cesm2/release_download.html, last access: 2 June 2023). The scripts used for the signal separation of the three ESMs, the evaluation and the energy balance decomposition can be found on the GitHub page of the hydrology department of VUB (https://github.com/VUB-HYDR/2022_De-Hertog_etal_ESD, De Hertog, 2022). The data analysed within this study can be found here: https://www.wdc-climate.de/ui/entry?acronym=DKRZ_LTA_1147_ds00001 (De Hertog, 2023). The simulation data used in this paper will be made available through the Deutsches Klimarechenzentrum (DKRZ); for those interested in using these data, please contact the authors.
CFS, QL, WT, DC, JP, ELD, SIS, FH, IM, SG and SJDH designed the simulation protocol. SG and FH performed the simulations with MPI-ESM. IM performed the simulations with EC-EARTH. SDH performed the simulations with CESM and the data analysis and wrote the paper. IV assisted with the setting up of the CESM simulations and with the data analysis. FH and SDH performed the post-processing for the signal separation. FL prepared the EC-EARTH data for post-processing and helped with the signal separation for EC-EARTH. ELD helped with the preparation of the land cover datasets. GD assisted with the model evaluation. All authors commented on the paper and provided feedback throughout the data analysis.
The contact author has declared that none of the authors has any competing interests.
Publisher’s note: Copernicus Publications remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
This work was funded by the DLR/German Federal Ministry of Education and Research (DE, grant no. 01LS1905A), the Dutch Research Council, and the Belgian Science Policy Office (BELSPO) and was co-funded by the European Union through the project “LAnd MAnagement for CLImate Mitigation and Adaptation” (LAMACLIMA) (grant agreement no. 300478), which is part of ERA4CS, an ERA-NET initiated by JPI Climate. Inne Vanderkelen is a research fellow at the Research Foundation Flanders (grant no. FWOTM920). Gregory Duveiller was supported by the European Research Council (ERC) Synergy Grant “Understanding and Modelling the Earth System with Machine Learning (USMILE)” under grant agreement no. 855187. The computational resources and services used in this work for the simulations and storage of CESM data were provided by the VSC (Flemish Supercomputer Center), funded by the Research Foundation – Flanders (FWO) and the Flemish Government – department EWI. For the storage of signal-separated results and the simulations of MPI-ESM, this work used the resources of the Deutsches Klimarechenzentrum (DKRZ), granted by its Scientific Steering Committee (WLA) under project no. bm1147. Fei Luo and Dim Coumou acknowledge the VIDI award from the Netherlands Organization for Scientific Research (NWO) (Persistent Summer Extremes “PERSIST” project no. 016.Vidi.171.011). Fei Luo would like to thank Philippe Le Sager, Lars Nieradzik and Thomas Reerink for their help in the discussions for the post-processing and interpretations of EC-EARTH model output. All the simulations from EC-EARTH were carried out on European Center for Medium Range Weather Forecast (ECMWF) platforms. The authors would like to thank Johannes Winckler, Lars Nieradzik, Paul Miller, David Wårlind and the reviewers for their constructive and useful feedback, which greatly helped to improve the paper during the review process. Finally, we thank the handling editor, Kirsten Zickfeld, for her constructive attitude and feedback throughout the review process.
This research has been funded by the Belgian Science Policy Office (BELSPO) and was co-funded by the European Union through the project “LAnd MAnagement for CLImate Mitigation and Adaptation” (LAMACLIMA) (grant agreement no. 300478), which is part of ERA4CS, an ERA-NET initiated by JPI Climate.
This paper was edited by Kirsten Zickfeld and reviewed by David Wårlind and one anonymous referee.
Akkermans, T., Thiery, W., and Van Lipzig, N. P.: The regional climate impact of a realistic future deforestation scenario in the congo basin, J. Clim., 27, 2714–2734, https://doi.org/10.1175/JCLI-D-13-00361.1, 2014. a
Al-Yaari, A., Ducharne, A., Thiery, W., Cheruy, F., and Lawrence, D.: The role of irrigation expansion on historical climate change: insights from CMIP6, Earth's Future, 10, e2022EF002859, https://doi.org/10.1029/2022EF002859, 2022. a, b
Alkama, R. and Cescatti, A.: Climate change: Biophysical climate impacts of recent changes in global forest cover, Science, 351, 600–604, https://doi.org/10.1126/science.aac8083, 2016. a, b, c, d, e, f, g, h, i, j, k
Arias, P., Bellouin, N., Coppola, E., Jones, R., Krinner, G., Marotzke, J., Naik, V., Palmer, M., Plattner, G., Rogelj, J., Rojas, M., Sillmann, J., Storelvmo, T. Thorne, P., Trewin, B. Achuta Rao, K., Adhikary, B., Allan, R., Armour, K.and Bala, G., Barimalala, R., Berger, S., Canadell, S., Cassou, C., Cherchi, A., Collins, W., Collins, W., Connors, S., Corti, S., Cruz, F., Dentener, F., Dereczynski, C., Di Luca, A., Diongue Niang, A., Doblas-Reyes, F., Dosio, A., Douville, F., Engelbrecht, F., Eyring, V., Fischer, E., Forster, P., Fox-Kemper, B., Fuglestvedt, J., Fyfe, J., Gillett, C., Goldfarb, L., Gorodetskaya, I., Gutierrez, J., Hamdi, R., Hawkins, E., Hewitt, H., Hope, P., Islam, H., Jones, C., Kaufman, D., Kopp, R., Kosaka, Y., Kossin, J., Krakovska, S., Lee, J.-Y., Li, Y. Mauritsen, T., T.K., M., Meinshausen, M. Min, S.-K., Monteiro, P., Ngo-Duc, T., Otto, F., Pinto, I., Pirani, A., Raghavan, K., R., R., Ruane, A., Ruiz, R., Sallé, R., Samset, B., Sathyendranath, S., Seneviratne, S.I. Sörensson, S. S. A., Takayabu, I. Tréguier, A., van den Hurk, B., Vautard, R., von Schuckmann, K., Zaehle, S., Zhang, X., and Zickfeld, K.: 2021: Technical Summary, in: Climate Change 2021: The Physical Science Basis, Contribution of Working Group I to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change, edited by: Masson-Delmotte, V., Zhai, P., Pirani, A., Connors, S. L., and Péan, C. S., Cambridge University Press, 150 pp., https://www.ipcc.ch/report/ar6/wg1/downloads/report/IPCC_AR6_WGI_TS.pdf (last access: 31 May 2023), 2021. a
Ban-Weiss, G. A., Bala, G., Cao, L., Pongratz, J., and Caldeira, K.: Climate forcing and response to idealized changes in surface latent and sensible heat, Environ. Res. Lett., 6, 034032, https://doi.org/10.1088/1748-9326/6/3/034032, 2011. a
Blyth, E. M., Arora, V. K., Clark, D. B., Dadson, S. J., De Kauwe, M. G., Lawrence, D. M., Melton, J. R., Pongratz, J., Turton, R. H., Yoshimura, K., and Yuan, H.: Advances in Land Surface Modelling, Curr. Clim. Change Rep., 7, 45–71, https://doi.org/10.1007/s40641-021-00171-5, 2021. a
Boisier, J. P., De Noblet-Ducoudré, N., Pitman, A. J., Cruz, F. T., Delire, C., Van Den Hurk, B. J., Van Der Molen, M. K., Mller, C., and Voldoire, A.: Attributing the impacts of land-cover changes in temperate regions on surface temperature and heat fluxes to specific causes: Results from the first LUCID set of simulations, J. Geophys. Res.-Atmos., 117, 1–16, https://doi.org/10.1029/2011JD017106, 2012. a
Boysen, L. R., Brovkin, V., Pongratz, J., Lawrence, D. M., Lawrence, P., Vuichard, N., Peylin, P., Liddicoat, S., Hajima, T., Zhang, Y., Rocher, M., Delire, C., Séférian, R., Arora, V. K., Nieradzik, L., Anthoni, P., Thiery, W., Laguë, M. M., Lawrence, D., and Lo, M. H.: Global climate response to idealized deforestation in CMIP6 models, Biogeosciences, 17, 5615–5638, https://doi.org/10.5194/bg-17-5615-2020, 2020. a, b, c, d, e, f
Bright, R. M., Davin, E., O'Halloran, T., Pongratz, J., Zhao, K., and Cescatti, A.: Local temperature response to land cover and management change driven by non-radiative processes, Nat. Clim. Change, 7, 296–302, https://doi.org/10.1038/nclimate3250, 2017. a, b, c, d, e, f, g, h, i, j, k
Canadell, J., Monteiro, P., Costra, M., Cotrim da Cunha, L., Cox, P., Eliseev, A., Henson, S., Ishii, M., Jaccard, S., Koven, C., Lohila, A., Patra, P., Piao, S., Rogelj, J., Syampungani, S., Zaehle, S., and Zickfeld, K.: Climate Change 2021: The Physical Science Basis, Contribution of Working Group I to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change, edited by: Masson-Delmotte, V., Zhai, P., Pirani, A., Connors, S. L., Péan, C., Berger, S., Caud, N., Chen, Y., Goldfarb, L., Gomis, M. I., Huang, M., Leitzell, K., Lonnoy, E., Matthews, J. B. R., Maycock, T. K., Waterfield, T., Yelekçi, O., Yu, R., and Zhou, B., Cambridge University Press, https://www.ipcc.ch/report/ar6/wg1/downloads/report/IPCC_AR6_WGI_TS.pdf (last access: 31 May 2023), 2021. a
Danabasoglu, G., Lamarque, J. F., Bacmeister, J., Bailey, D. A., DuVivier, A. K., Edwards, J., Emmons, L. K., Fasullo, J., Garcia, R., Gettelman, A., Hannay, C., Holland, M. M., Large, W. G., Lauritzen, P. H., Lawrence, D. M., Lenaerts, J. T., Lindsay, K., Lipscomb, W. H., Mills, M. J., Neale, R., Oleson, K. W., Otto-Bliesner, B., Phillips, A. S., Sacks, W., Tilmes, S., van Kampenhout, L., Vertenstein, M., Bertini, A., Dennis, J., Deser, C., Fischer, C., Fox-Kemper, B., Kay, J. E., Kinnison, D., Kushner, P. J., Larson, V. E., Long, M. C., Mickelson, S., Moore, J. K., Nienhouse, E., Polvani, L., Rasch, P. J., and Strand, W. G.: The Community Earth System Model Version 2 (CESM2), J. Adv. Model. Earth Syst., 12, 1–35, https://doi.org/10.1029/2019MS001916, 2020. a, b
Davin, E. L. and de Noblet-Ducoudre, N.: Climatic impact of global-scale Deforestation: Radiative versus nonradiative processes, J. Clim., 23, 97–112, https://doi.org/10.1175/2009JCLI3102.1, 2010. a, b, c, d
Davin, E. L., Rechid, D., Breil, M., Cardoso, R. M., Coppola, E., Hoffmann, P., Jach, L. L., Katragkou, E., De Noblet-Ducoudré, N., Radtke, K., Raffa, M., Soares, P. M., Sofiadis, G., Strada, S., Strandberg, G., Tölle, M. H., Warrach-Sagi, K., and Wulfmeyer, V.: Biogeophysical impacts of forestation in Europe: First results from the LUCAS (Land Use and Climate across Scales) regional climate model intercomparison, Earth Syst. Dynam., 11, 183–200, https://doi.org/10.5194/esd-11-183-2020, 2020. a
De Hertog, S.: VUB-HYDR/2022_De-Hertog_etal_ESD, Github [data set], https://github.com/VUB-HYDR/2022_De-Hertog_etal_ESD (last access: 2 June 2023), 2022. a
De Hertog, S.: Postprocessed data of LAMACLIMA simulations underlying the analysis done in De Hertog et al. (2022) ESD, DOKU at DKRZ [data set], https://www.wdc-climate.de/ui/entry?acronym=DKRZ_LTA_1147_ds00001 (last access: 31 May 2023), 2023. a
De Noblet-Ducoudré, N., Boisier, J. P., Pitman, A., Bonan, G. B., Brovkin, V., Cruz, F., Delire, C., Gayler, V., Van Den Hurk, B. J., Lawrence, P. J., Van Der Molen, M. K., Müller, C., Reick, C. H., Strengers, B. J., and Voldoire, A.: Determining robust impacts of land-use-induced land cover changes on surface climate over North America and Eurasia: Results from the first set of LUCID experiments, J. Clim., 25, 3261–3281, https://doi.org/10.1175/JCLI-D-11-00338.1, 2012. a
Döscher, R., Acosta, M., Alessandri, A., Anthoni, P., Arsouze, T., Bergman, T., Bernardello, R., Boussetta, S., Caron, L.-P., Carver, G., Castrillo, M., Catalano, F., Cvijanovic, I., Davini, P., Dekker, E., Doblas-Reyes, F. J., Docquier, D., Echevarria, P., Fladrich, U., Fuentes-Franco, R., Gröger, M., v. Hardenberg, J., Hieronymus, J., Karami, M. P., Keskinen, J.-P., Koenigk, T., Makkonen, R., Massonnet, F., Ménégoz, M., Miller, P. A., Moreno-Chamarro, E., Nieradzik, L., van Noije, T., Nolan, P., O'Donnell, D., Ollinaho, P., van den Oord, G., Ortega, P., Prims, O. T., Ramos, A., Reerink, T., Rousset, C., Ruprich-Robert, Y., Le Sager, P., Schmith, T., Schrödner, R., Serva, F., Sicardi, V., Sloth Madsen, M., Smith, B., Tian, T., Tourigny, E., Uotila, P., Vancoppenolle, M., Wang, S., Wårlind, D., Willén, U., Wyser, K., Yang, S., Yepes-Arbós, X., and Zhang, Q.: The EC-Earth3 Earth system model for the Coupled Model Intercomparison Project 6, Geosci. Model Dev., 15, 2973–3020, https://doi.org/10.5194/gmd-15-2973-2022, 2022. a, b, c
Duveiller, G., Hooker, J., and Cescatti, A.: The mark of vegetation change on Earth’s surface energy balance, Nat. Commun., 9, p. 679, https://doi.org/10.1038/s41467-017-02810-8, 2018. a, b, c, d, e, f, g, h, i
Duveiller, G., Caporaso, L., Abad-Viñas, R., Perugini, L., Grassi, G., Arneth, A., and Cescatti, A.: Local biophysical effects of land use and land cover change: towards an assessment tool for policy makers, Land Use Pol., 91, 104382, https://doi.org/10.1016/j.landusepol.2019.104382, 2020. a, b, c, d, e, f, g, h
Duveiller, G., Filipponi, F., Ceglar, A., Bojanowski, J., Alkama, R., and Cescatti, A.: Revealing the widespread potential of forests to increase low level cloud cover, Nat. Commun., 12, 1–15, https://doi.org/10.1038/s41467-021-24551-5, 2021. a, b
Erb, K.-H., Kastner, C., Plutzar, W., Bais, A., Carvalhais, N., Fetzel, T., Gingrich, S., Haberl, H., Lauk, C., Niedertscheider, M., Pongratz, J., Thurner, M., and Luyssaert, S.: Unexpectedly large impact of forest management and grazing on global vegetation biomass, Nature, 553, 73–76, 2018. a
European Commission: The European Green Deal, COM(2019) 640 final, https://commission.europa.eu/strategy-and-policy/priorities-2019-2024/european-green-deal_en (last access: 5 June 2023), 2019. a
Friedlingstein, P., Jones, M. W., O'Sullivan, M., Andrew, R. M., Bakker, D. C. E., Hauck, J., Le Quéré, C., Peters, G. P., Peters, W., Pongratz, J., Sitch, S., Canadell, J. G., Ciais, P., Jackson, R. B., Alin, S. R., Anthoni, P., Bates, N. R., Becker, M., Bellouin, N., Bopp, L., Chau, T. T. T., Chevallier, F., Chini, L. P., Cronin, M., Currie, K. I., Decharme, B., Djeutchouang, L. M., Dou, X., Evans, W., Feely, R. A., Feng, L., Gasser, T., Gilfillan, D., Gkritzalis, T., Grassi, G., Gregor, L., Gruber, N., Gürses, Ö., Harris, I., Houghton, R. A., Hurtt, G. C., Iida, Y., Ilyina, T., Luijkx, I. T., Jain, A., Jones, S. D., Kato, E., Kennedy, D., Klein Goldewijk, K., Knauer, J., Korsbakken, J. I., Körtzinger, A., Landschützer, P., Lauvset, S. K., Lefèvre, N., Lienert, S., Liu, J., Marland, G., McGuire, P. C., Melton, J. R., Munro, D. R., Nabel, J. E. M. S., Nakaoka, S.-I., Niwa, Y., Ono, T., Pierrot, D., Poulter, B., Rehder, G., Resplandy, L., Robertson, E., Rödenbeck, C., Rosan, T. M., Schwinger, J., Schwingshackl, C., Séférian, R., Sutton, A. J., Sweeney, C., Tanhua, T., Tans, P. P., Tian, H., Tilbrook, B., Tubiello, F., van der Werf, G. R., Vuichard, N., Wada, C., Wanninkhof, R., Watson, A. J., Willis, D., Wiltshire, A. J., Yuan, W., Yue, C., Yue, X., Zaehle, S., and Zeng, J.: Global Carbon Budget 2021, Earth Syst. Sci. Data, 14, 1917–2005, https://doi.org/10.5194/essd-14-1917-2022, 2022. a
Gormley-Gallagher, A. M., Sterl, S., Hirsch, A. L., Seneviratne, S. I., Davin, E. L., and Thiery, W.: Agricultural management effects on mean and extreme temperature trends, Earth Syst. Dynam., 13, 419–438, https://doi.org/10.5194/esd-13-419-2022, 2022. a
Guimberteau, M., Laval, K., Perrier, A., and Polcher, J.: Global effect of irrigation and its impact on the onset of the Indian summer monsoon, Clim. Dynam., 39, 1329–1348, https://doi.org/10.1007/s00382-011-1252-5, 2012. a
Haddeland, I., Heinke, J., Biemans, H., Eisner, S., Flörke, M., Hanasaki, N., Konzmann, M., Ludwig, F., Masaki, Y., Schewe, J., Stacke, T., Tessler, Z. D., Wada, Y., and Wisser, D.: Global water resources affected by human interventions and climate change, P. Natl. Acad. Sci. USA, 111, 3251–3256, https://doi.org/10.1073/pnas.1222475110, 2014. a
Hauser, M., Thiery, W., and Isabelle Seneviratne, S.: Potential of global land water recycling to mitigate local temperature extremes, Earth Syst. Dynam., 10, 157–169, https://doi.org/10.5194/esd-10-157-2019, 2019. a
Hirsch, A. L., Wilhelm, M., Davin, E. L., Thiery, W., and Seneviratne, S. I.: Can climate-effective land management reduce regional warming?, J. Geophys. Res., 122, 2269–2288, https://doi.org/10.1002/2016JD026125, 2017. a, b
Hirsch, A. L., Prestele, R., Davin, E. L., Seneviratne, S. I., Thiery, W., and Verburg, P. H.: Modelled biophysical impacts of conservation agriculture on local climates, Glob. Change Biol., 24, 4758–4774, https://doi.org/10.1111/gcb.14362, 2018. a
Humpenöder, F., Popp, A., and Dietrich, J. P.: Investigating afforestation and bioenergy CCS as climate change mitigation strategies, Environ. Res. Lett., 9, 064029, https://doi.org/10.1088/1748-9326/9/6/064029, 2014. a
Hurtt, G. C., Chini, L., Sahajpal, R., Frolking, S., Bodirsky, B. L., Calvin, K., Doelman, J. C., Fisk, J., Fujimori, S., Klein Goldewijk, K., Hasegawa, T., Havlik, P., Heinimann, A., Humpenöder, F., Jungclaus, J., Kaplan, J. O., Kennedy, J., Krisztin, T., Lawrence, D., Lawrence, P., Ma, L., Mertz, O., Pongratz, J., Popp, A., Poulter, B., Riahi, K., Shevliakova, E., Stehfest, E., Thornton, P., Tubiello, F. N., van Vuuren, D. P., and Zhang, X.: Harmonization of global land use change and management for the period 850–2100 (LUH2) for CMIP6, Geosci. Model Dev., 13, 5425–5464, https://doi.org/10.5194/gmd-13-5425-2020, 2020. a, b
IPCC: Global Warming of 1.5 ∘C. An IPCC Special Report on the impacts of global warming of 1.5 ∘C above pre-industrial levels and related global greenhouse gas emission pathways, in the context of strengthening the global response to the threat of climate change,, Tech. Rep., https://doi.org/10.1038/291285a0, 2018. a
Ito, A., Hajima, T., Lawrence, D. M., Brovkin, V., Delire, C., Guenet, B., Jones, C. D., Malyshev, S., Materia, S., McDermid, S. P., Peano, D., Pongratz, J., Robertson, E., Shevliakova, E., Vuichard, N., Wårlind, D., Wiltshire, A., and Ziehn, T.: Soil carbon sequestration simulated in CMIP6-LUMIP models: Implications for climatic mitigation, Environ. Res. Lett., 15, 124061, https://doi.org/10.1088/1748-9326/abc912, 2020. a
Juang, J. Y., Katul, G., Siqueira, M., Stoy, P., and Novick, K.: Separating the effects of albedo from eco-physiological changes on surface temperature along a successional chronosequence in the southeastern United States, Geophys. Res. Lett., 34, 1–5, https://doi.org/10.1029/2007GL031296, 2007. a, b
Kumar, S., Dirmeyer, P. A., Merwade, V., Delsole, T., Adams, J. M., and Niyogi, D.: Land use/cover change impacts in CMIP5 climate simulations: A new methodology and 21st century challenges, J. Geophys. Res.-Atmos., 118, 6337–6353, https://doi.org/10.1002/jgrd.50463, 2013. a, b
Lawrence, D. M., Hurtt, G. C., Arneth, A., Brovkin, V., Calvin, K. V., Jones, A. D., Jones, C. D., Lawrence, P. J., de Noblet-Ducoudré, N., Pongratz, J., Seneviratne, S. I., and Shevliakova, E.: The Land Use Model Intercomparison Project (LUMIP) contribution to CMIP6: rationale and experimental design, Geosci. Model Dev., 9, 2973–2998, https://doi.org/10.5194/gmd-9-2973-2016, 2016. a, b
Lawrence, D. M., Fisher, R. A., Koven, C. D., Oleson, K. W., Swenson, S. C., Bonan, G., Collier, N., Ghimire, B., van Kampenhout, L., Kennedy, D., Kluzek, E., Lawrence, P. J., Li, F., Li, H., Lombardozzi, D., Riley, W. J., Sacks, W. J., Shi, M., Vertenstein, M., Wieder, W. R., Xu, C., Ali, A. A., Badger, A. M., Bisht, G., van den Broeke, M., Brunke, M. A., Burns, S. P., Buzan, J., Clark, M., Craig, A., Dahlin, K., Drewniak, B., Fisher, J. B., Flanner, M., Fox, A. M., Gentine, P., Hoffman, F., Keppel-Aleks, G., Knox, R., Kumar, S., Lenaerts, J., Leung, L. R., Lipscomb, W. H., Lu, Y., Pandey, A., Pelletier, J. D., Perket, J., Randerson, J. T., Ricciuto, D. M., Sanderson, B. M., Slater, A., Subin, Z. M., Tang, J., Thomas, R. Q., Val Martin, M., and Zeng, X.: The Community Land Model Version 5: Description of New Features, Benchmarking, and Impact of Forcing Uncertainty, J. Adv. Model. Earth Syst., 11, 4245–4287, https://doi.org/10.1029/2018MS001583, 2019. a, b, c
Lejeune, Q., Davin, E. L., Guillod, B. P., and Seneviratne, S. I.: Influence of Amazonian deforestation on the future evolution of regional surface fluxes, circulation, surface temperature and precipitation, Clim. Dynam., 44, 2769–2786, https://doi.org/10.1007/s00382-014-2203-8, 2015. a
Lejeune, Q., Seneviratne, S. I., and Davin, E. L.: Historical land-cover change impacts on climate: Comparative assessment of LUCID and CMIP5 multimodel experiments, J. Clim., 30, 1439–1459, https://doi.org/10.1175/JCLI-D-16-0213.1, 2017. a, b
Li, Y., Zhao, M., Motesharrei, S., Mu, Q., Kalnay, E., and Li, S.: Local cooling and warming effects of forests based on satellite observations, Nat. Commun., 6, 6603, https://doi.org/10.1038/ncomms7603, 2015. a, b, c, d, e, f, g, h, i, j, k, l
Lindeskog, M., Arneth, A., Bondeau, A., Waha, K., Seaquist, J., Olin, S., and Smith, B.: Implications of accounting for land use in simulations of ecosystem carbon cycling in Africa, Earth Syst. Dynam., 4, 385–407, https://doi.org/10.5194/esd-4-385-2013, 2013. a
Luyssaert, S., Jammet, M., Stoy, P. C., Estel, S., Pongratz, J., Ceschia, E., Churkina, G., Don, A., Erb, K., Ferlicoq, M., Gielen, B., Grünwald, T., Houghton, R. A., Klumpp, K., Knohl, A., Kolb, T., Kuemmerle, T., Laurila, T., Lohila, A., Loustau, D., McGrath, M. J., Meyfroidt, P., Moors, E. J., Naudts, K., Novick, K., Otto, J., Pilegaard, K., Pio, C. A., Rambal, S., Rebmann, C., Ryder, J., Suyker, A. E., Varlagin, A., Wattenbach, M., and Dolman, A. J.: Land management and land-cover change have impacts of similar magnitude on surface temperature, Nat. Clim. Change, 4, 389–393, https://doi.org/10.1038/nclimate2196, 2014. a, b, c
Mahmood, R., Pielke, R. A., Hubbard, K. G., Niyogi, D., Dirmeyer, P. A., Mcalpine, C., Carleton, A. M., Hale, R., Gameda, S., Beltrán-Przekurat, A., Baker, B., Mcnider, R., Legates, D. R., Shepherd, M., Du, J., Blanken, P. D., Frauenfeld, O. W., Nair, U. S., and Fall, S.: Land cover changes and their biogeophysical effects on climate, Int. J. Climatol., 34, 929–953, https://doi.org/10.1002/joc.3736, 2014. a
Malyshev, S., Shevliakova, E., Stouffer, R. J., and Pacala, S. W.: Contrasting local versus regional effects of land-use-change-induced heterogeneity on historical climate: Analysis with the GFDL earth system model, J. Clim., 28, 5448–5469, https://doi.org/10.1175/JCLI-D-14-00586.1, 2015. a, b
Mauritsen, T., Bader, J., Becker, T., Behrens, J., Bittner, M., Brokopf, R., Brovkin, V., Claussen, M., Crueger, T., Esch, M., Fast, I., Fiedler, S., Fläschner, D., Gayler, V., Giorgetta, M., Goll, D. S., Haak, H., Hagemann, S., Hedemann, C., Hohenegger, C., Ilyina, T., Jahns, T., Jimenéz-de-la Cuesta, D., Jungclaus, J., Kleinen, T., Kloster, S., Kracher, D., Kinne, S., Kleberg, D., Lasslop, G., Kornblueh, L., Marotzke, J., Matei, D., Meraner, K., Mikolajewicz, U., Modali, K., Möbis, B., Müller, W. A., Nabel, J. E., Nam, C. C., Notz, D., Nyawira, S. S., Paulsen, H., Peters, K., Pincus, R., Pohlmann, H., Pongratz, J., Popp, M., Raddatz, T. J., Rast, S., Redler, R., Reick, C. H., Rohrschneider, T., Schemann, V., Schmidt, H., Schnur, R., Schulzweida, U., Six, K. D., Stein, L., Stemmler, I., Stevens, B., von Storch, J. S., Tian, F., Voigt, A., Vrese, P., Wieners, K. H., Wilkenskjeld, S., Winkler, A., and Roeckner, E.: Developments in the MPI-M Earth System Model version 1.2 (MPI-ESM1.2) and Its Response to Increasing CO2, J. Adv. Model. Earth Syst., 11, 998–1038, https://doi.org/10.1029/2018MS001400, 2019. a
Meier, R., Davin, E. L., Lejeune, Q., Hauser, M., Li, Y., Martens, B., Schultz, N. M., Sterling, S., and Thiery, W.: Evaluating and improving the Community Land Model's sensitivity to land cover, Biogeosciences, 15, 4731–4757, https://doi.org/10.5194/bg-15-4731-2018, 2018. a, b, c
Meier, R., Schwaab, J., Seneviratne, S. I., Sprenger, M., Lewis, E., and Davin, E. L.: Empirical estimate of forestation-induced precipitation changes in Europe, Nat. Geosci., 14, 473–478, https://doi.org/10.1038/s41561-021-00773-6, 2021. a
Minx, J. C., Lamb, W. F., Callaghan, M. W., Fuss, S., Hilaire, J., Creutzig, F., Amann, T., Beringer, T., De Oliveira Garcia, W., Hartmann, J., Khanna, T., Lenzi, D., Luderer, G., Nemet, G. F., Rogelj, J., Smith, P., Vicente Vicente, J. L., Wilcox, J., and Del Mar Zamora Dominguez, M.: Negative emissions – Part 1: Research landscape and synthesis, Environ. Res. Lett., 13, 063001, https://doi.org/10.1088/1748-9326/aabf9b, 2018. a
Mishra, V., Ambika, A. K., Asoka, A., Aadhar, S., Buzan, J., Kumar, R., and Huber, M.: Moist heat stress extremes in India enhanced by irrigation, Nat. Geosci., 13, 722–728, https://doi.org/10.1038/s41561-020-00650-8, 2020. a, b
Nakai, T., Sumida, A., Daikoku, K., Matsumoto, K., van der Molen, M. K., Kodama, Y., Kononov, A. V., Maximov, T. C., Dolman, A. J., Yabuki, H., Hara, T., and Ohta, T.: Parameterisation of aerodynamic roughness over boreal, cool- and warm-temperate forests, Agr. Forest Meteorol., 148, 1916–1925, https://doi.org/10.1016/j.agrformet.2008.03.009, 2008. a
Otto, J., Berveiller, D., Bréon, F. M., Delpierre, N., Geppert, G., Granier, A., Jans, W., Knohl, A., Kuusk, A., Longdoz, B., Moors, E., Mund, M., Pinty, B., Schelhaas, M. J., and Luyssaert, S.: Forest summer albedo is sensitive to species and thinning: How should we account for this in Earth system models?, Biogeosciences, 11, 2411–2427, https://doi.org/10.5194/bg-11-2411-2014, 2014. a
Perugini, L., Caporaso, L., Marconi, S., Cescatti, A., Quesada, B., De Noblet-Ducoudré, N., House, J. I., and Arneth, A.: Biophysical effects on temperature and precipitation due to land cover change, Environ. Res. Lett., 12, 053002, https://doi.org/10.1088/1748-9326/aa6b3f, 2017. a, b
Pitman, A. J., De Noblet-Ducoudré, N., Cruz, F. T., Davin, E. L., Bonan, G. B., Brovkin, V., Claussen, M., Delire, C., Ganzeveld, L., Gayler, V., Van Den Hurk, B. J., Lawrence, P. J., Van Der Molen, M. K., Müller, C., Reick, C. H., Seneviratne, S. I., Strengen, B. J., and Voldoire, A.: Uncertainties in climate responses to past land cover change: First results from the LUCID intercomparison study, Geophys. Res. Lett., 36, 1–6, https://doi.org/10.1029/2009GL039076, 2009. a, b
Pongratz, J., Reick, C. H., Raddatz, T., and Claussen, M.: Biogeophysical versus biogeochemical climate response to historical anthropogenic land cover change, Geophys. Res. Lett., 37, 1–5, https://doi.org/10.1029/2010GL043010, 2010. a
Pongratz, J., Schwingshackl, C., Bultan, S., Obermeier, W., Havermann, F., and Guo, S.: Land Use Effects on Climate: Current State, Recent Progress, and Emerging Topics, Curr. Clim. Change Rep., 6, 1–22, https://doi.org/10.1007/s40641-021-00178-y, 2021. a
Roe, S., Streck, C., Obersteiner, M., Frank, S., Griscom, B., Drouet, L., Fricko, O., Gusti, M., Harris, N., Hasegawa, T., Hausfather, Z., Havlík, P., House, J., Nabuurs, G. J., Popp, A., Sánchez, M. J. S., Sanderman, J., Smith, P., Stehfest, E., and Lawrence, D.: Contribution of the land sector to a 1.5 ∘C world, Nat. Clim. Change, 9, 817–828, https://doi.org/10.1038/s41558-019-0591-9, 2019. a
Rosa, L., Chiarelli, D. D., Sangiorgio, M., Beltran-Peña, A. A., Rulli, M. C., D'Odorico, P., and Fung, I.: Potential for sustainable irrigation expansion in a 3 ∘C warmer climate, P. Natl. Acad. Sci. USA, 117, 29526–29534, https://doi.org/10.1073/pnas.2017796117, 2020. a
Sanderman, J., Hengl, T., and Fiske, G. J.: Soil carbon debt of 12,000 years of human land use, P. Natl. Acad. Sci. USA, 114, 9575–9580, 2017. a
Smith, B., Wårlind, D., Arneth, A., Hickler, T., Leadley, P., Siltberg, J., and Zaehle, S.: Implications of incorporating N cycling and N limitations on primary production in an individual-based dynamic vegetation model, Biogeosciences, 11, 2027–2054, https://doi.org/10.5194/bg-11-2027-2014, 2014. a
Smith, P., Davis, S. J., Creutzig, F., Fuss, S., Minx, J., Gabrielle, B., Kato, E., Jackson, R. B., Cowie, A., Kriegler, E., Vuuren, D. P. V., Rogelj, J., Ciais, P., Milne, J., Canadell, J. G., McCollum, D., Peters, G., Andrew, R., Krey, V., Shrestha, G., Friedlingstein, P., Gasser, T., Grübler, A., Heidug, W. K., Jonas, M., Jones, C. D., Kraxner, F., Littleton, E., Lowe, J., Moreira, J. R., Nakicenovic, N., Obsersteiner, M., Patwardhan, A., Rogner, M., Rubin, E., Sharifi, A., Torvanger, A., Yamagata, Y., Edmonds, J., and Yongsung, C.: Biophysical and economic limits to negative CO2 emissions, Nat. Clim. Change, 6, 42–50, https://doi.org/10.1038/nclimate2870, 2015. a
Teuling, A. J., Taylor, C. M., Meirink, J. F., Melsen, L. A., Miralles, D. G., Van Heerwaarden, C. C., Vautard, R., Stegehuis, A. I., Nabuurs, G. J., and De Arellano, J. V. G.: Observational evidence for cloud cover enhancement over western European forests, Nat. Commun., 8, 1–7, https://doi.org/10.1038/ncomms14065, 2017. a
Thiery, W., Davin, E. L., Lawrence, D. M., Hirsch, A. L., Hauser, M., and Seneviratne, S. I.: Present-day irrigation mitigates heat extremes, J. Geophys. Res., 122, 1403–1422, https://doi.org/10.1002/2016JD025740, 2017. a, b, c, d, e
Thiery, W., Visser, A. J., Fischer, E. M., Hauser, M., Hirsch, A. L., Lawrence, D. M., Lejeune, Q., Davin, E. L., and Seneviratne, S. I.: Warming of hot extremes alleviated by expanding irrigation, Nat. Commun., 11, 1–7, https://doi.org/10.1038/s41467-019-14075-4, 2020. a, b
van Maanen, N., Andrijevic, M., Lejeune, Q., Rosa, L., Lissner, T., and Schleussner, C. F.: Accounting for socioeconomic constraints in sustainable irrigation expansion assessments, Environ. Res. Lett., 17, 075004, https://doi.org/10.1088/1748-9326/ac77a5, 2022. a
Vanderkelen, I., Lipzig, N. P. M., Sacks, W. J., Lawrence, D. M., Clark, M. P., Mizukami, N., Pokhrel, Y., and Thiery, W.: Simulating the Impact of Global Reservoir Expansion on the Present‐Day Climate, J. Geophys. Res.-Atmos., 126, e2020JD034485, https://doi.org/10.1029/2020jd034485, 2021. a
Winckler, J., Reick, C. H., and Pongratz, J.: Robust identification of local biogeophysical effects of land-cover change in a global climate model, J. Clim., 30, 1159–1176, https://doi.org/10.1175/JCLI-D-16-0067.1, 2017. a, b, c, d, e, f, g, h, i, j
Winckler, J., Lejeune, Q., Reick, C. H., and Pongratz, J.: Nonlocal Effects Dominate the Global Mean Surface Temperature Response to the Biogeophysical Effects of Deforestation, Geophys. Res. Lett., 46, 745–755, https://doi.org/10.1029/2018GL080211, 2019a. a, b, c, d, e, f, g, h, i, j, k
Winckler, J., Reick, C. H., Bright, R. M., and Pongratz, J.: Importance of Surface Roughness for the Local Biogeophysical Effects of Deforestation, J. Geophys. Res.-Atmos., 124, 8605–8618, https://doi.org/10.1029/2018JD030127, 2019b. a, b, c, d, e
Winckler, J., Reick, C. H., Luyssaert, S., Cescatti, A., Stoy, P. C., Lejeune, Q., Raddatz, T., Chlond, A., Heidkamp, M., and Pongratz, J.: Different response of surface temperature and air temperature to deforestation in climate models, Earth Syst. Dynam., 10, 473–484, https://doi.org/10.5194/esd-10-473-2019, 2019c. a, b, c, d, e
Windisch, M. G., Davin, E. L., and Seneviratne, S. I.: Prioritizing forestation based on biogeochemical and local biogeophysical impacts, Nat. Clim. Change, 11, 867–871, https://doi.org/10.1038/s41558-021-01161-z, 2021. a