Dieter Gerten’s research while affiliated with Humboldt-Universität zu Berlin and other places

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Publications (242)


A software package for assessing terrestrial planetary boundaries
  • Article

June 2025

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21 Reads

One Earth

Dieter Gerten

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Johanna Braun

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[...]

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Global net carbon dioxide removal and biomass plantation area under incremental and isolated consideration of terrestrial planetary boundary constraints
Impact of planetary boundary (PB) constraints on net carbon dioxide removal (CDR) (a) and biomass plantation area (b). See Tables 1 and 2 for the definitions of scenarios and PB constraints (N nitrogen flows, W freshwater change, L land system change, B biosphere integrity, FP forest protection as a stricter definition of the land system change PB). Under these constraints, the distribution of biomass plantations was optimized to maximize net CDR while reserving current agricultural areas for food, fodder and fiber provision. Relative changes refer to the unconstrained CDRonly scenario. For CDR, numbers in brackets depict the range spanned by using inputs from five general circulation models for mid-century climate under RCP4.5 and three carbon removal efficiency pathways (optimal, moderate, low; assuming a biomass-to-electricity conversion). The coloring visualizes the numbers relative to the column’s respective maximum values.
Optimized global distribution of biomass plantations to maximize net carbon dioxide removal
Optimized biomass plantation distributions are shown for scenarios without (CDRonly; panel a) and with individual planetary boundary (PB) constraints for nitrogen flows (N), freshwater change (W), land system change (L), or biosphere integrity (B) (panels b–e). Under PB constraints, plantation expansion and/or management is limited by the respective PB thresholds (see Table 1); agricultural areas are safeguarded for food, fodder, and fiber production, and wetlands, urban, and protected areas are excluded from conversion. Colors refer to the share of irrigated vs rainfed (irr. share) and fertilized vs. unfertilized (fert. share) biomass plantations, while the color’s transparency represents the cell fraction covered with biomass plantations.
Global net carbon dioxide removal from expanding biomass plantations for BECCS under consideration of planetary boundary constraints
a Impacts of incremental consideration of planetary boundary (PB) constraints on global BECCS potential. Net carbon dioxide removal (CDR) is displayed for three carbon removal efficiency (CEff) pathways (optimal, moderate, low, assuming a biomass-to-electricity conversion). The error bars reflect the range based on mid-century RCP4.5 climate change scenarios from five general circulation models (2036–2065). Percentage changes refer to the relative incremental effect of each constraint. b Projected CDR demand in scenarios likely limiting warming to <2 °C (C1–C3) included in IPCC’s 6th assessment report (AR6)¹, boxplots show median and interquartile ranges for 2050 and 2100 respectively (see Supplementary Methods). c Single mean effect of the PB constraints relative to the unconstrained CDRonly scenario.
Cumulative emissions and carbon payback period
a Cumulative emissions for the unconstrained CDRonly scenario and the allPBs scenario, where all terrestrial planetary boundary (PB) constraints are considered. The lines refer to the mean; the shading gives the range for the input from five climate models. The carbon payback period, i.e., the number of years needed to compensate for the initial land use change emissions, is displayed as values in boxes for three carbon removal efficiencies (CEff; low, moderate, optimistic) assuming a biomass-to-electricity conversion. Additional plots for all scenarios can be found in Supplementary Fig. 13. b Spatially-explicit carbon payback period under a moderate CEff in the unconstrained CDRonly scenario, averaged for five general circulation models under mid-century RCP4.5 climate.
Multiple planetary boundaries preclude biomass crops for carbon capture and storage outside of agricultural areas
  • Article
  • Full-text available

February 2025

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90 Reads

Six of nine planetary boundaries are currently transgressed, many related to human land use. Conversion of sizeable land areas to biomass plantations for Bioenergy with Carbon Capture and Storage (BECCS) – often assumed in climate mitigation scenarios to meet the Paris Agreement – may exert additional pressure on terrestrial planetary boundaries. Using spatially-explicit, process-based global biogeochemical modelling, we systematically compute feedstock production potentials for BECCS under individual and joint constraints of the planetary boundaries for nitrogen flows, freshwater change, land system change and biosphere integrity (including protection of remaining forests), while reserving current agricultural areas for meeting the growing global demand for food, fodder and fibre. We find that the constrained BECCS potential from dedicated Miscanthus plantations is close to zero (0.1 gigatons of carbon dioxide equivalents per year under mid-century climate for Representative Concentration Pathway (RCP) 4.5). The planetary boundary for biosphere integrity has the largest individual effect, highlighting a particularly severe trade-off between climate change mitigation with BECCS and ecosystem preservation. Ultimately however, the overall limitation results from the joint effect of all four planetary boundaries, emphasizing the importance of a holistic consideration of Earth system stability in the context of climate change mitigation.

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Intensified dominance of El Niño-like convection relevant for global atmospheric circulation variations

December 2024

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154 Reads

Tropical convection anomaly could serve as a crucial driver of global atmospheric teleconnections and weather extremes around the world. However, quantifying the dominances of convection anomalies with regional discrepancies, relevant for the variations of global atmospheric circulations, remains challenging. By using a network analysis of observation-based CMAP rainfall and ERA5 reanalysis datasets, our study reveals that El Niño-like convection is the most primary rainfall pattern driving the global circulation variations. Furthermore, we find that the global climate relevance of El Niño-like convection will be doubled by the end of this century, as projected consistently by 23 climate models. Such “rich nodes get richer” phenomenon in the network science is probably attributable to the dipolar rainfall changes over the western-central Pacific, coupled with the projected El Niño-like sea surface temperature changes. This study highlights the dominant role of El Niño-like convection on the global climate variations, especially under the future changing climate.


Figure 5: Global area with transgression of local boundaries of EcoRisk (boundary, 0.35; high-risk zone, 0.55) and HANPP Hol (0.05; 0.23) combined. The intermediate and high risk status is assigned if at least one of the two thresholds is crossed. For the high risk status, we display a confidence interval as the Q25 -Q75 threshold ranges (EcoRisk: 0.54 -0.59, HANPP Hol : 0.18 -0.32). For time series of EcoRisk and HANPP Hol individually see Figure A3. Biome specific area transgressed is shown in Figure A4.
Mapping the Transgression of the Planetary Boundary for Functional Biosphere Integrity

October 2024

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225 Reads

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1 Citation

Two new control variables are suggested for quantitatively assessing the core planetary boundary for functional biosphere integrity: 1) Human appropriation of net primary production (HANPP) and 2) a metric for ecological disruption (EcoRisk). HANPP is a measure of the pressure exerted on the biosphere by removing energy otherwise available to ecosystem processes. EcoRisk indicates ecological disequilibrium through changes in vegetation structure and biogeochemical state variables as a measure of more general ecological disruption. We use simulations with the Dynamic Global Vegetation Model LPJmL to map the status of these variables at a spatial resolution of 0.5◦ x0.5◦ and quantify their temporal evolution since the year 1600. We additionally quantify local thresholds using a newly developed methodology at grid-cell scale by comparison with independent indicators for biosphere integrity. We find that EcoRisk and HANPP are good predictors of degradation as measured by a variety of global ecological datasets. We finally combine both indicators into a meta-metric, and aggregate results globally to a planetary boundary status based on the land area showing a transgression of the local thresholds relative to the preindustrial state. We find that the local boundary is currently transgressed on 69% of the global ice-free land surface, with 44% already at high risk of degradation.



Geographical distances of weather extremes
Probability density function (PDF) for the distance of significant links in (a) heat-heat daily concurrence networks (red line with solid circles) and heat-cold daily concurrence networks (blue line with hollow circles), (b) heat-high daily concurrence networks (red line with solid circles) and heat-low daily concurrence networks (blue line with hollow circles), and (c) heat-high interannual correlation networks (red line with solid circles) and heat-low interannual correlation networks (blue line with hollow circles). Networks in (b, c) are constructed between weather extremes based on air temperature at 2 m (T2m\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${T}_{2m}$$\end{document}) and geopotential height at 500 hPa (H500\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$H500$$\end{document}). The significant p-values are shown in the upper right labels in (a–c). The links with link strengths L(a,b)≤80\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${L}_{(a,{b})}\le 80$$\end{document} for the two networks in (b) are considered as weak links and thus removed. The vertical dashed green lines in (a–c) denote the distances of 1500 km and 4000 km.
Linkage between heatwaves and atmospheric teleconnections (AT)
Composite anomalies of (a, d) air temperature at 2 m (T2m\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${T}_{2m}$$\end{document}; shadings; units: K) and atmospheric circulations at 500 hPa (UV500; vectors; units: m s⁻¹), and (b, e) geopotential height (H500; shadings; units: gpm) and wave flux activity (WAF500; vectors; units: m² s⁻²) at 500 hPa. a, b are the composite anomalies for Eastern European heatwave events, while (d, e) are for Western European heatwave events. Cross-degree centrality of high-pressure extremes (shadings; units:×1000) inside (c) Eastern European heatwaves and (f) Western European heatwaves. Cross-degree centrality of low-pressure extremes (blue dashed contours) for Eastern European heatwaves (shown at 42,000 and 50,000) and Western European heatwaves (shown at 21,000 and 25,000) are also plotted in (c) and (f), respectively. g Explained variance (R2\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${R}^{2}$$\end{document}) of yearly heatwave cumulative intensity (HWI) by AT, and h the zonal median in explained variance (red solid line). R\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$R$$\end{document} is the correlation coefficient between the yearly detrended time series of HWI and AT at each grid cell. The zonal median in explained variance between HWI and similar AT index using only local high-pressure intensities is also plotted as orange dashed line in (h). Significant values (p<0.05\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$p < 0.05$$\end{document}) are hatched and insignificant vectors are not plotted in (a, b) and (d, e). The wave activity fluxes are not shown when both directions of the values are less than 0.5 m² s⁻² or both wind component (u\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$u$$\end{document} and v\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$v$$\end{document}) anomalies are insignificant. The red dashed lines in (a) and (d) denote the regions that are 2700 km and 5200 km far away from the centers of Eastern and Western European land areas, respectively. Yearly explained variances in (g) are positive over all grid cells and significant (R2>0.147,p<0.01\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${R}^{2} > 0.147,{p} < 0.01$$\end{document}) over 99.8% of the land areas.
Zonally asymmetric trends in heatwave cumulative intensity (HWI) attributable to atmospheric teleconnections (AT)
a Observed zonally asymmetric trends (observed trends minus their zonal mean) in HWI. b Estimated HWI trends by AT. c Regional observed (filled bars) and estimated (hatched bars) zonally asymmetric trends in HWI averaged over Northwestern North America (NWNA), Eastern North America (ENA), Western Europe (WE), Europe (including Western Europe and Eastern Europe), Eastern Europe (EE), South Asia-central Asia (SCA), Eastern Asia (EA), and Northeastern Asia (NEA). d Proportion (units: %) of land area (gray thin line) with the same signs between observed zonally asymmetric trend and estimated trend, and its 11-degree running average (green thick line). Probability density function (PDF; units: 1) of normalized HWI during the periods of 1979–2000 (orange dashed lines) and 2001–2022 (red solid lines) in (e) all grid cells, (f) grid cells where estimated trend is greater than 2, and (g) grid cells where estimated trend is less than -2, in mid-latitude land areas (40°–65°N). Units of HWI trend in (a–c) are K decade⁻¹. Red (blue) hatched areas in (b) represent the areas with correct signs estimated by AT with accelerated (mitigated) HWI trends. The signs of negative observed zonally asymmetric and estimated trends (blue bars) are reversed in (c). Colored solid, half solid, and hollow circles in (c) denote the trends in AT over the corresponding regions significant at the 99%, 95%, 90% confidence levels, respectively. See methods for the specific areas of different regions. Before calculating PDF in (e–g), normalized HWI is standardized by subtracting the average and dividing the standard deviation obtained from the period of 1979–2000.
Accelerated increasing trends in European heatwaves linked to the amplified atmospheric teleconnections (AT)
Observed zonally asymmetric trends (units: gpm decade⁻¹) in (a) high-pressure intensity and (b) low-pressure intensity. Number of most-connected high-pressure (red markers) and low-pressure (green markers) grid cells (units: 1) for (c) Western and (d) Eastern European heatwaves. Normalized time series of gPCwest\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${{PC}}_{{west}}$$\end{document} and hPCeast\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${{PC}}_{{east}}$$\end{document}, which are the principal components associated to the leading EOF mode for V500 over the Western-Europe extended region (20°–70°N, 45°W–30°E) and Eastern-Europe extended region (20°–70°N, 20°–90°E), respectively. Regressed patterns of heatwave cumulative intensity (HWI; shadings; units: K) and atmospheric circulations at 500 hPa (vectors; units: m s⁻¹) onto ePCwest\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${{PC}}_{{west}}$$\end{document} and fPCeast\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${{PC}}_{{east}}$$\end{document}. Significant trends (p<0.1\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$p < 0.1$$\end{document}) and significant anomalies (p<0.05\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$p < 0.05$$\end{document}) are hatched in (a, b) and (e, f), respectively. Only the significant atmospheric circulations (p<0.05\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$p < 0.05$$\end{document}) are plotted in (e, f). Western Europe (WE; 35°–55°N, 10°W–25°E) and Eastern Europe (EE; 45°–65°N, 25°–55°E) are outlined by the red boxes in (a). Northeastern Atlantic (40°–60°N, 45°W–0°), northern Africa (22°–38°N, 5°–25°E), central Asia-central Russia (25°–60°N, 58°–85°E, and 60°–75°N, 58°–102°E) are outlined by the blue boxes in (b–d). The red boxes in (e, f) present the domains of Western-Europe extended region and Eastern-Europe extended region for EOF analysis.
Simulated trends in Eastern European heatwaves linked to the atmospheric teleconnections (AT) in CMIP6 models
Simulated differences in zonally asymmetric trends between the high-EE-trend group and the low-EE-trend group for a the heatwave cumulative intensity (HWI; units: K decade⁻¹) and b the difference between high-pressure and low-pressure intensities (units: gpm decade⁻¹). The high-EE-trend (low-EE-trend) group includes 8 models simulating the highest (lowest) Eastern European asymmetric HWI trends. Significant differences (p<0.05\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$$p < 0.05$$\end{document}) are hatched in (a, b). Simulated zonally asymmetric trends in HWI versus c high-pressure intensity, and (d) mean intensities between high-pressure and low-pressure extremes in 29 CMIP6 models. Results obtained from the ERA5 reanalysis dataset are also provided in (c, d). The high-pressure intensity in (c, d) is averaged over Eastern Europe (45°–65°N, 25°–55°E), while the low-pressure intensity is averaged over the northeastern Atlantic (45°–60°N, 30°W–0°) and Western Asia (30°–45°N, 55°–75°E). The x-axis units for (c, d) are K decade⁻¹, while the y-axis units are gpm year⁻¹. The red boxes in (a, b) present the domain of Eastern Europe, while blue boxes in (b) present the domains of Northeastern Atlantic and Western Asia. The labels denoting the 29 models and the ERA5 trends are shown in the rightmost corner.
Sketching the spatial disparities in heatwave trends by changing atmospheric teleconnections in the Northern Hemisphere

September 2024

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539 Reads

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13 Citations

Pronounced spatial disparities in heatwave trends are bound up with a diversity of atmospheric signals with complex variations, including different phases and wavenumbers. However, assessing their relationships quantitatively remains a challenging problem. Here, we use a network-searching approach to identify the strengths of heatwave-related atmospheric teleconnections (AT) with ERA5 reanalysis data. This way, we quantify the close links between heatwave intensity and AT in the Northern Hemisphere. Approximately half of the interannual variability of heatwaves is explained and nearly 80% of the zonally asymmetric trend signs are estimated correctly by the AT changes in the mid-latitudes. We also uncover that the likelihood of extremely hot summers has increased sharply by a factor of 4.5 after 2000 over areas with enhanced AT, but remained almost unchanged over the areas with attenuated AT. Furthermore, reproducing Eastern European heatwave trends among various models of the Coupled Model Intercomparison Project Phase 6 largely depends on the simulated Eurasian AT changes, highlighting the potentially significant impact of AT shifts on the simulation and projection of heatwaves.


Figure 1: Overview of the basic workflow providing LPJmL biosphere model outputs (left panel) to the boundaries software package (right panel). Outputs, i.e. PB control variables, are needed for a pre-industrial reference period and any later period for which PB statuses are to be analysed. They are transformed by boundaries to PB statuses according to given PB definitions and parameter thresholds, for different scales (grid, regional, global), and eventually plotted as maps or time series graphs.
Definitions, values and spatial analysis scales of planetary and regional control vari- ables considered. Numbers in brackets: upper end of increasing risk zone. n.d. = not defined/used here.
A Software Package for Assessing Terrestrial Planetary Boundaries

July 2024

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73 Reads

Abstract There is a dearth of assessments of temporal trajectories and spatial patterns of planetary boundaries (PBs – precautionary limits to human interference with nine critical Earth system processes). To facilitate such studies by a generic computation tool, we have developed the R-based, open-source software package ‘boundaries’. It allows to calculate and plot the statuses of different PBs (i.e. if, when, where, and how strongly they are transgressed), based on required variables provided from an external source. The pilot version 1.0 presented here is designed to use outputs from the LPJmL biosphere model, which dynamically simulates processes underlying the PBs for land-system change, freshwater change, nitrogen flows and biosphere integrity. From these data, boundaries derives the four PBs’ statuses at different scales (planetary and corresponding regional boundaries), in a transparent way, following the latest definitions. In an application, we visualise the past and current PB states. We strongly encourage users to enhance boundaries for processing outputs from other models and datasets. Keywords: planetary boundaries, LPJmL, Earth system, analysis software


Planetary boundary interaction simulation set-up. LPJmL5.1 is forced by SSP5-RCP8.5 scenario climate forcings provided by ten different GCMs from the CMIP6 ensemble (solid black line) succeeding the historical CO2 forcing (solid gray line). The blue dot represents the ‘current’ value for the year 2015 (398 ppm). Five ppm levels representing different statuses of the planetary boundary for climate change (ranging from ‘safe’ green to ‘unsafe’ red) were taken and held constant by recycling and shuffling a 20 yr window of surrounding climate and CO2 concentrations (colored rectangles). Changes resulting by the end of the century and millennium were assessed in the status of the land-system change boundary, and in the freshwater, climate change and biosphere integrity boundaries. In parallel to the historical forcing, a potential natural vegetation simulation was conducted to assess the undisturbed status of the land-system change boundary as the reference case.
Forest biome extent under potential natural vegetation, and the current status of the land-system change boundary. (a) Potential forest biome extent without land use and pre-industrial climate (mean 1850–1859), representing the reference status for the land-system change boundary. Biome classification based on Ostberg et al (2013) and described in SI. Only cells with GCM-forcing agreement of >30% are shown. (b) Current status (mean 2005–2014) of the land-system change boundary, based on the share of remaining forest biome in each continent of figure 2(a). Green areas are below the boundary; other areas have breached the planetary boundary and are subject to increasing risk (yellow) or high risk (red). Planetary boundary threshold values taken from (Steffen et al 2015, Richardson et al 2023).
Effects of transgressions of the climate change boundary on the status of the land-system change boundary. The bold vertical lines indicate biome-specific planetary boundaries (Steffen et al 2015). They delineate the safe operating space for the forest cover extent (green areas to the left) from the increasing risk and high risk zones (yellow and red areas to the right). The x-axis indicates the scenario forest extent relative to PNV, theoretically ranging from 100% (biome extent as under PNV) to 0% (no PNV forest cover remaining). To improve the readability, the x-axis was adjusted for each biome. The interquartile ranges capture the variations of the biome-specific land-system change boundary status for the ten GCM forcings for both the year 2100 and 3000, with the circle marking the median.
Simulated changes in forest biome area, ensemble median. (a) Latitude shifts of forest ecosystems by the end of the millennium, based on percentage change in biome area. While negative values indicate a loss, positive values describe a gain of the specific forest biome at the latitude under a particular scenario (irrespective of the PNV extent). (b) Biome areas under PNV, currently, as well as under different levels of the climate change boundary (by 3000). The size of the circles corresponds with the area of the biome (in Mha). The inner lighter circles indicate the remainder of the PNV biome and the darker color the biome area shifted beyond this extent.
Changes in the status of other planetary boundaries under the 750 ppm scenario between their current status (mean 2005–2014) and the simulation period around year 3000 (mean 2996–3005). Only changes in forested areas (under 750 ppm) are shown where >30% of the model ensemble is in agreement and where anthropogenic land-use constitutes less than 40% of a cell’s area (in 2015). (a) & (b) Biome shift with red colors indicating a high GCM agreement of forest loss and blue colors a gain in forest for boreal forest (a) and temperate forest (b). (c) Habitat intactness change, depicting changes in plant composition in areas characterized by still integer ecosystems with a high biosphere integrity index (BII, Newbold et al 2016). (d) Changes in root-zone soil moisture, where red colors indicate a drying, blue a wetting trend (annual average). (e) Absolute surface albedo changes, where red colors indicate a reduction in albedo (darker surfaces). (f) Changes in net biome productivity, where red colors indicate a weakening of the terrestrial carbon sink. (c) Is chosen as a proxy for the biosphere integrity boundary, (d) represents the freshwater change boundary) while both (e) and (f) indicate biophysical feedbacks to the climate change boundary (see SI for details).
Climate change critically affects the status of the land-system change planetary boundary

May 2024

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411 Reads

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2 Citations

The planetary boundaries framework defines a safe operating space for humanity. To date, these boundaries have mostly been investigated separately, and it is unclear whether breaching one boundary can lead to the transgression of another. By employing a dynamic global vegetation model, we systematically simulate the strength and direction of the effects of different transgression levels of the climate change boundary (using climate output from ten phase 6 of the Coupled Model Intercomparison Project models for CO2 levels ranging from 350 ppm to 1000 ppm). We focus on climate change-induced shifts of Earth’s major forest biomes, the control variable for the land-system change boundary, both by the end of this century and, to account for the long-term legacy effect, by the end of the millennium. Our simulations show that while staying within the 350 ppm climate change boundary co-stabilizes the land-system change boundary, breaching it (>450 ppm) leads to critical transgression of the latter, with greater severity the higher the ppm level rises and the more time passes. Specifically, this involves a poleward treeline shift, boreal forest dieback (nearly completely within its current area under extreme climate scenarios), competitive expansion of temperate forest into today’s boreal zone, and a slight tropical forest extension. These interacting changes also affect other planetary boundaries (freshwater change and biosphere integrity) and provide feedback to the climate change boundary itself. Our quantitative process-based study highlights the need for interactions to be studied for a systemic operationalization of the planetary boundaries framework.


Calculation scheme for BioCol. The basis for our analysis is the preindustrial potential NPP (NPPref) assessed from 1550–1579. The effects of CO2 fertilization of plants resulting from historical anthropogenic CO2 emissions, changes in atmospheric N deposition, and climate change lead to a net increase in NPP today (labeled as the “CC effect” in the biosphere) both for hypothetical “potential vegetation” without human land use and the “actual vegetation” including land use. HANPP is calculated as the sum of direct human biomass extraction (NPPharv) and inhibited natural productivity through replacing natural vegetation with land use (NPPluc=NPPpot-NPPact). BioCol is subsequently computed as the fraction of HANPP compared to NPPref.
(a) Global BioCol and components over time. BioCol values use the orange axis on the right and are calculated as a sum of absolute values (“BioCol abs sum” – cells with negative value increase the global sum) or simple sum (“BioCol sum” – cells with negative value reduce the global sum). (b) Map of the relative values for the year 2000 (average 1995–2005). Relative values for BioCol are expressed in comparison to the average NPP from 1550–1579 from a run without human land use.
(a) Change in biochemical compositions computed by EcoRisk between 1550–1579 and 1985–2016. (b) Current land use extent for reference. (c–f) EcoRisk components are as follows: vegetation structure change, local change, global importance, ecosystem balance.
(a) Present (1987–2016) biomes classified from vegetation structure, plant-specific leaf area index, temperature and elevation in LPJmL5. (b) Change in biochemical compositions computed by EcoRisk between 1550–1579 and 1985–2016 as the median (Q10 and Q90 for whiskers) across the 16 most relevant biomes (“Temperate Broadleaved Evergreen Forest” is effectively non-existent as only two cells are classified as such, while “Rocks and Ice” and “Water” are skipped for lack of vegetation). See Table for biome names and abbreviations.
Contextualization of several indicators of biosphere integrity, transformed to the interval [0,1], with 0 meaning high integrity, no pressure, and low risk: (a) GLASOD representing human-induced soil degradation , (b) HF representing human footprint , (c) BII representing the biodiversity intactness index , (d) intactness representing GLOBIOM 2015 MSA , (e) FLII representing the Forest Landscape Intactness Index , (f) CI representing contextual intactness , (g) CoE representing the Convergence of Evidence from World Atlas of Desertification . (h) The number of the previous seven indicators that show up as transgressed per grid cell (see Table for thresholds indicating transition between low- and high-risk zones), (i) EcoRisk and (j) BioCol (l) average of metrics shown in (a)–(g), (k) scatterplot of EcoRisk versus average, and (m) scatterplot of BioCol versus average.
biospheremetrics v1.0.2: an R package to calculate two complementary terrestrial biosphere integrity indicators – human colonization of the biosphere (BioCol) and risk of ecosystem destabilization (EcoRisk)

April 2024

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98 Reads

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4 Citations

Ecosystems are under multiple stressors, and impacts can be measured with multiple variables. Humans have altered mass and energy flows of basically all ecosystems on Earth towards dangerous levels. However, integrating the data and synthesizing conclusions is becoming more and more complicated. Here we present an automated and easy-to-apply R package to assess terrestrial biosphere integrity that combines two complementary metrics. (i)The BioCol metric that quantifies the human colonization pressure exerted on the biosphere through alteration and extraction (appropriation) of net primary productivity. (ii)The EcoRisk metric that quantifies biogeochemical and vegetation structural changes as a proxy for the risk of ecosystem destabilization. Applied to simulations with the dynamic global vegetation model LPJmL5 for 1500–2016, we find that large regions presently (period 2007–2016) show modification and extraction of >20 % of the preindustrial potential net primary production. The modification (degradation) of net primary production (NPP) as a result of land use change and extraction in terms of biomass removal (e.g., from harvest) leads to drastic alterations in key ecosystem properties, which suggests a high risk of ecosystem destabilization. As a consequence of these dynamics, EcoRisk shows particularly high values in regions with intense land use and deforestation and in regions prone to impacts of climate change, such as the Arctic and boreal zone. The metrics presented here enable spatially explicit global-scale evaluation of historical and future states of the biosphere and are designed for use by the wider scientific community, being applicable not only to assessing biosphere integrity but also to benchmarking model performance. The package will be maintained on GitHub and through that we encourage its future application to other models and data sets.


Pronounced spatial disparity of projected heatwave changes in the Northern Hemisphere linked to heat domes and soil moisture-temperature coupling

April 2024

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Heatwaves are projected to substantially increase almost without exception at a global scale, exacerbating worldwide heat-related risks in the future. However, understanding spatial heterogeneity of future heatwave changes and their origins remains challenging. By analyzing the output of various climate models from the Coupled Model Intercomparison Project Phase 6, we found pronounced spatial disparity of projected heatwave increases in the Northern Hemisphere, even outstretching ten-fold inter-regional differences in extreme heatwave occurrences, attributed primarily to future changes in heat-dome-like circulations and soil moisture-temperature coupling. Specifically, we found that by the end of the 21st century, the modulations of combined Pacific El Niño and positive Pacific Meridional Mode on magnified heat-dome-like circulations would be translated into summertime hotspots over western Asia and western North America. Amplified soil moisture-temperature couplings then further aggravate the heatwave intensity over these two hotspots. This study of future heterogeneous heatwave patterns provides supports for formulating impact-based mitigation strategies and efficiently addressing the potential future risks for climate extremes.


Citations (70)


... Due to geographical differences and the multifactorial influence of socioeconomic activities, the risk of heat waves is not spatially uniform [37]. In this study, we selected Dongcheng, Xicheng, Fengtai, Haidian, Chaoyang, and Fangshan to ensure sample diversity ( Figure 1). ...

Reference:

Differential Impacts on Human Physiological Responses on Heatwave and Non-Heatwave Days: A Comparative Study Using Wearable Devices in Beijing
Pronounced spatial disparity of projected heatwave changes linked to heat domes and land-atmosphere coupling

npj Climate and Atmospheric Science

... Human appropriation of net primary production (NPP) as a percentage of preindustrial NPP (max. 10%, assessed by biomes, n = 61) 30,57 Planetary boundary (PB) definitions for nitrogen flows, freshwater change, land system change, and biosphere integrity, including the spatial scale of the assessment for constraining the expansion and management of biomass plantations for bioenergy with carbon capture and storage (BECCS). N nitrogen. ...

biospheremetrics v1.0.2: an R package to calculate two complementary terrestrial biosphere integrity indicators – human colonization of the biosphere (BioCol) and risk of ecosystem destabilization (EcoRisk)

... Prolonged heating causes the atmosphere to store energy, increasing the likelihood of extreme rainfall shortly after a heatwave ends 5 . Under climate change, the frequency of both heatwaves and extreme rainfall has increased [6][7][8][9][10][11][12] . During the summer of 2023, China experienced 14 extreme heat events, with about 70% of national weather stations recording temperatures above 40°C 13 . ...

Sketching the spatial disparities in heatwave trends by changing atmospheric teleconnections in the Northern Hemisphere

... The status of terrestrial PBs is not only impacted by land use but also by climate change [63][64][65] . In addition to transgressions caused by agriculture, we, therefore, also accounted for the impacts of~2°C warming when evaluating constraints on biomass plantation expansion and management. ...

Climate change critically affects the status of the land-system change planetary boundary

... Currently, human activities such as intensive fossil use are causing widespread changes in the atmosphere, land, oceans and cryosphere (Kloenne et al., 2023;Porkka et al., 2024;Zhu et al., 2024). Human activities compete with geophysical processes, resulting in declines in the global supply of natural resources and ability to absorb pollutants (Arrow et al., 1995;Han et al., 2024). ...

Notable shifts beyond pre-industrial streamflow and soil moisture conditions transgress the planetary boundary for freshwater change

Nature Water

... Rainfall is an important atmospheric input for land hydrological cycle and plays a crucial role for food production and ecosystem services. For instance, in the CRB, more than 80% of agriculture is rainfed 11 , leaving its population in a position of high food insecurity and vulnerability to climate change 12 . Rainfall also sustains the Congo rainforests and, depending on the climatic context, prevents the transition to a savannah state [13][14][15][16] . ...

African rainforest moisture contribution to continental agricultural water consumption

Agricultural and Forest Meteorology

... The same input datasets were used for all scenarios. We used the climate data from the GSWP3-W5E5 dataset (Kim;Cucchi et al., 2020;Lange et al., 2022), historical atmospheric N deposition , historical atmospheric CO 2 concentrations (Büchner and Reyer, 2022), historical land-use patterns and grazing management data (Stenzel et al., 2023). For both BNF approaches, we conducted spinup simulations of 3500 years using a random permutation of the climate data from 1901 to 1931. ...

biospheremetrics v1.0.1: An R package to calculate two complementary terrestrial biosphere integrity indicators: human colonization of the biosphere (BioCol) and risk of ecosystem destabilization (EcoRisk)

... Earth ecosystems are increasingly impacted by human activities and climate change, leading to widespread declines in intra-and interspecific organismal diversity (Luypaert et al. 2020;Exposito-Alonso et al. 2022;Richardson et al. 2023). A valuable-yet often poorly communicated-lesson from recent conservation and management efforts is that it is possible to turn the tide if species are adequately protected and given space and time to recover. ...

Earth beyond six of nine planetary boundaries

Science Advances

... However, the extreme temperatures, increased hydrological variability, shifts in atmospheric rivers, and continental drying anticipated in the Anthropocene are external forces that may inhibit regime change (Rockström et al 2023). It will be increasingly difficult for some cities currently in Phase 1 to make the transition to Phase 2 because more capital and better institutions will be needed. ...

Why we need a new economics of water as a common good

Nature

... RA is a form of sustainable agriculture that has emerged as one potential answer to the detrimental developments in agricultural systems presented in Chapter 1.1. RA can have a broad variety of foci, ranging from soil regeneration (Schreefel et al., 2020;Sherwood & Uphoff, 2000), and climate change mitigation (Gosnell et al., 2019;Lal, 2020) to food security and resilience in agricultural systems (Breier et al., 2023). ...

Regenerative agriculture for food security and ecological resilience: illustrating global biophysical and social spreading potentials (Earth4All deep dive report)