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Modelling long-term, large-scale sediment dynamics in an
Earth System Model framework
- PhD Disputation -
Victoria Naipal
12.01.2016
1st Evaluator: Prof. Dr. Martin Claußen
2nd Evaluator: Dr. Christian Reick
1/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
“A nation that destroys its soils destroys itself” – U.S. President Franklin D. Roosevelt
Soil erosion and land use change during the
last millennium for the Rhine catchmentSevere soil erosion on agricultural land
In Ethiopia
Source: www.mikegoldwater.com
Soil erosion and land use change
Bare
Grass
Forest
Crop + pasture
2/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Missing soil erosion related carbon exchange fluxes
Source: Ciais et al., 2014
Knowledge gaps
3/28
 Large uncertainty in global soil erosion rates: 20 - 200 Pg y-1 (Doetterl et al, 2012)
 Sediment deposition and transport fluxes are unknown on the global scale
(Hoffmann et al., 2013)
 The effect of soil erosion and sediment dynamics on global biogeochemical
cycles is unknown (Quinton et al., 2010)
 Earth System Models (ESMs) ignore erosion and sediment dynamics and
miss an important aspect of the coupling between land and the ocean
(Van Oost et al., 2012)
 This hampers the quantification of the anthropogenic impact on the
biogeochemical cycles (Regnier et al., 2013)
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Modelling soil erosion and sediment dynamics
4/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Outline
Part 1
Improvement and validation of an existing soil erosion model
Part 2
Development and validation of a new global sediment budget model
Part 3
Possible impacts of soil erosion on the biogeochemical cycles
Are the effects of soil erosion and associated sediment dynamics on the
biogeochemical cycles globally significant?
Modelling soil erosion on a global scale
5/28
Objective
To develop a global soil erosion model to quantify erosion rates for present
day and for the last millennium.
Research Questions
1. How can we model local scale soil erosion on the global scale?
2. Can the global soil erosion rates be reproduced with data from ESMs?
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
The Universal Soil Loss Equation (RUSLE) model (Renard et al., 1997)
6/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
 Average annual soil erosion rate (t ha-1 y-1) =
Topography (S) * Rainfall erosivity (R) * Land cover (C) * Soil erodibility (K)
* support practice (P) * slope-length (L)
Naipal et al., 2015 (GMD)
The adjusted RUSLE model (Naipal et al., 2015)
7/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Naipal et al., 2015 (GMD)
1. Improvement of the S factor
• Slope is poorly estimated from coarse resolution global digital
elevation models (DEMs)
• The slope can be upscaled to 150 m using the fractal method
2. Improvement of the R factor
• Multiple linear regression approach
R = f(P)  R = f(P, z, I)
• Climate zones of the Köppen-Geiger climate classification
𝑆 = 𝛼𝑑1−𝐷
S = slope
D = grid resolution
α, D = fractal parameters
P = total yearly precipitation
z = mean elevation
I = precipitation intensity index
Experimental setup with the adj. RUSLE model
8/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Naipal et al., 2015 (GMD)
Simulation using data from observational datasets
• Climate: GPCC (0.25o), CLIMDEX (2.5o), Köppen-Geiger classification (0.083o)
• Land cover and land use: GIMMS (0.25o), MODIS (0.25o)
• Topography: GTOPO (0.0083o~1 km)
• Soil: GSCE and HWSD (0.0083o~1 km)
Simulations using data from ESMs (CMIP5)
• Models: MPI-ESM (1.875o), IPSL-CM5A (3.75o), CCSM4 (1.25o), MIROC-ESM
and bcc-csm1 (2.81o)
• Climate and land cover/use data from the models
• Topography and soil data from observational datasets
Present-day global soil erosion rates - adjusted RUSLE model
(Naipal et al., 2015)
9/28
Mean: 6.5 t ha-1 y-1
Uncertainty mean: 5.3 -15 t ha-1 y-1
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Naipal et al., 2015 (GMD)
Present-day erosion rates: Model input vs. observation input
10/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Simulation with model data
Simulation with observational data
Summary
11/28
1. How can we model local scale soil erosion on the global scale?
• The adjusted RUSLE model reproduces present-day soil erosion rates
for Europe and the USA
2. Can the global soil erosion rates be reproduced with data from ESMs?
• Soil erosion rates derived from observational data can be reproduced
using CMIP5 data, however, there is some uncertainty
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
I made the RUSLE model applicable on a coarse resolution on the
global scale, however, the model is very sensitive to the climate and
land cover data from ESMs
Conclusion
Modelling sediment dynamics on a global scale
12/28
Objective
To develop a global model for sediment dynamics to quantify long-term
changes in sediment fluxes
Research Questions
1. How can we model long-term large-scale sediment dynamics?
2. How did sediment storage change during the last millennium and what
were the main drivers?
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
The new sediment budget model
13/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Flow routing scheme
Naipal et al., 2015 (Esurf, under revision)
Erosion (E(t)) = S * R * C * K
Ma(t+1) = Ma(t) + deposition fraction( fa(t+1) ) * E(t+1) – Loss ( L(t) )
L (t) = Ma(t) / residence time (τ)
Mc(t+1) = Mc(t) + deposition fraction( fc(t+1) ) * E(t+1)
Experimental setup for simulating sediment budgets during the
last millennium (850 – 2005 AD)
14/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Naipal et al., 2015 (Esurf, under revision)
 Case studies:
• Rhine catchment
• Global
 Climate and land cover/use data from MPI-ESM-LR (last millennium +
historical experiments)
 Equilibrium simulation with mean climate and landcover conditions from
850-950 AD
 Transient simulations:
1. CC+LUC: Climate and land use change
2. CC: Climate change only (land use from 850AD)
3. LUC: Land use change only (climate from 850AD)
 Change in sediment storage during the transient simulation
The Rhine catchment
15/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Naipal et al., 2015 (Esurf, under revision)
Rhine catchment validation: Scaling behavior
16/28
𝐷𝑎𝑡𝑎: 𝑆𝑡𝑜𝑟𝑎𝑔𝑒~𝐵𝑎𝑠𝑖𝑛 𝑎𝑟𝑒𝑎1.23±0.06
𝐷𝑎𝑡𝑎: 𝑆𝑡𝑜𝑟𝑎𝑔𝑒~𝐵𝑎𝑠𝑖𝑛 𝑎𝑟𝑒𝑎1.06±0.07
For floodplains:
For hillslopes:
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Naipal et al., 2015 (Esurf, under revision)
𝑀𝑜𝑑𝑒𝑙: 𝑆𝑡𝑜𝑟𝑎𝑔𝑒~𝐵𝑎𝑠𝑖𝑛 𝑎𝑟𝑒𝑎1.2±0.04
𝑀𝑜𝑑𝑒𝑙: 𝑆𝑡𝑜𝑟𝑎𝑔𝑒~𝐵𝑎𝑠𝑖𝑛 𝑎𝑟𝑒𝑎1.05±0.06
Rhine catchment validation: Millennial sediment storage
17/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Observations versus model for Rhine sub-catchments
Naipal et al., 2015 (Esurf, under revision)
1:1 line
trend line
rmse=3.58
Global: Millennial sediment storage
18/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Global: Most sediment stored on hillslopes
19/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Global validation: Modelled vs. observed sediment yield
20/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
trend line
1:1 line
* Observed yields from Land2Sea database
Peuker-Ehrenbrink (2009)
rmse= 252
Global: Land use as the main contributor to sediment fluxes
21/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Simulation I
CC + LUC
ΔM = 6526 Gt
Simulation II
CC
ΔM = 5483 Gt
ΔM = 6658 Gt
Simulation III
LUC
Ganges
Amazon
Yellow
Nile
Mississippi
Summary
22/28
1. How can we model long-term large-scale sediment dynamics?
• The new sediment budget model reproduces the sediment storage
change in the Rhine catchment and sediment yields globally
2. How did sediment storage change during the last millennium and what
were the main drivers?
• Sediment storage increased significantly during the last millennium for
different global catchments, mainly due to land use change
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Conclusion
I developed a globally applicable sediment budget model, which shows
that land use change is the main driver behind the change in sediment
storage during the last millennium
Laterally displaced carbon and nutrients
23/28
Objective
To estimate the effect of soil erosion on the lateral fluxes of carbon and
nutrients
Research Questions
1. How large are present-day lateral fluxes of carbon and nutrients due to soil
erosion only ?
2. How much of the eroded carbon and nutrients is exported by rivers?
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
Present-day eroded soil organic carbon (SOC)
24/28
SOC erosion rate (Esoc) = E * area-weighted SOC%
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
g m-2 y-1
Esoc flux: 5.1 Pg C y-1  Esoc emissions: 1.0 Pg C y-1 ~ 13% of
fossil fuel emissions: 7.8 Pg C y-1
 River flux: 3% of Esoc
g m-2 y-1
Present-day eroded nitrogen
25/28
N erosion rate (En) = E * area-weighted N%
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
En flux: 336 Tg N y-1 ~ fertilizer use + fixation + deposition: 341 Tg N y-1
 River flux: 4% of En
Present-day eroded phosphorus
26/28
P erosion rate (Ep) = E * area-weighted P%
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
g m-2 y-1
Ep flux: 94 Tg P y-1 > fertilizer use + weathering: 50 Tg P y-1
 River flux: 7% of Ep
Summary
27/28
1. How large are present-day lateral fluxes of carbon and nutrients due to
soil erosion only ?
• Soil erosion results in significant fluxes of carbon and nutrients
globally
2. How much of the eroded carbon and nutrients is exported by rivers?
• Only a small part of the mobilized carbon and nutrients is exported by
rivers
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
I show that soil erosion and associated sediment dynamics should not
be neglected in studying the global biogeochemical cycles
Conclusion
 I developed the first dynamical global sediment budget model that
reproduces the global features of sediment dynamics
 I show that the effects of soil erosion and associated sediment
dynamics on the biogeochemical cycles are globally significant and
should not be neglected
Overall Conclusions
28/28
INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
 Implementing the sediment budget model in MPI-ESM and other ESMs
 Coupling the sediment budget model with the biogeochemical
components of ESMs
 Include other types of soil erosion: landslides, gullying, glacial erosion
Outlook

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Disputation_VN3_short

  • 1. Modelling long-term, large-scale sediment dynamics in an Earth System Model framework - PhD Disputation - Victoria Naipal 12.01.2016 1st Evaluator: Prof. Dr. Martin Claußen 2nd Evaluator: Dr. Christian Reick
  • 2. 1/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS “A nation that destroys its soils destroys itself” – U.S. President Franklin D. Roosevelt Soil erosion and land use change during the last millennium for the Rhine catchmentSevere soil erosion on agricultural land In Ethiopia Source: www.mikegoldwater.com Soil erosion and land use change Bare Grass Forest Crop + pasture
  • 3. 2/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Missing soil erosion related carbon exchange fluxes Source: Ciais et al., 2014
  • 4. Knowledge gaps 3/28  Large uncertainty in global soil erosion rates: 20 - 200 Pg y-1 (Doetterl et al, 2012)  Sediment deposition and transport fluxes are unknown on the global scale (Hoffmann et al., 2013)  The effect of soil erosion and sediment dynamics on global biogeochemical cycles is unknown (Quinton et al., 2010)  Earth System Models (ESMs) ignore erosion and sediment dynamics and miss an important aspect of the coupling between land and the ocean (Van Oost et al., 2012)  This hampers the quantification of the anthropogenic impact on the biogeochemical cycles (Regnier et al., 2013) INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
  • 5. Modelling soil erosion and sediment dynamics 4/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Outline Part 1 Improvement and validation of an existing soil erosion model Part 2 Development and validation of a new global sediment budget model Part 3 Possible impacts of soil erosion on the biogeochemical cycles Are the effects of soil erosion and associated sediment dynamics on the biogeochemical cycles globally significant?
  • 6. Modelling soil erosion on a global scale 5/28 Objective To develop a global soil erosion model to quantify erosion rates for present day and for the last millennium. Research Questions 1. How can we model local scale soil erosion on the global scale? 2. Can the global soil erosion rates be reproduced with data from ESMs? INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
  • 7. The Universal Soil Loss Equation (RUSLE) model (Renard et al., 1997) 6/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS  Average annual soil erosion rate (t ha-1 y-1) = Topography (S) * Rainfall erosivity (R) * Land cover (C) * Soil erodibility (K) * support practice (P) * slope-length (L) Naipal et al., 2015 (GMD)
  • 8. The adjusted RUSLE model (Naipal et al., 2015) 7/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Naipal et al., 2015 (GMD) 1. Improvement of the S factor • Slope is poorly estimated from coarse resolution global digital elevation models (DEMs) • The slope can be upscaled to 150 m using the fractal method 2. Improvement of the R factor • Multiple linear regression approach R = f(P)  R = f(P, z, I) • Climate zones of the Köppen-Geiger climate classification 𝑆 = 𝛼𝑑1−𝐷 S = slope D = grid resolution α, D = fractal parameters P = total yearly precipitation z = mean elevation I = precipitation intensity index
  • 9. Experimental setup with the adj. RUSLE model 8/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Naipal et al., 2015 (GMD) Simulation using data from observational datasets • Climate: GPCC (0.25o), CLIMDEX (2.5o), Köppen-Geiger classification (0.083o) • Land cover and land use: GIMMS (0.25o), MODIS (0.25o) • Topography: GTOPO (0.0083o~1 km) • Soil: GSCE and HWSD (0.0083o~1 km) Simulations using data from ESMs (CMIP5) • Models: MPI-ESM (1.875o), IPSL-CM5A (3.75o), CCSM4 (1.25o), MIROC-ESM and bcc-csm1 (2.81o) • Climate and land cover/use data from the models • Topography and soil data from observational datasets
  • 10. Present-day global soil erosion rates - adjusted RUSLE model (Naipal et al., 2015) 9/28 Mean: 6.5 t ha-1 y-1 Uncertainty mean: 5.3 -15 t ha-1 y-1 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Naipal et al., 2015 (GMD)
  • 11. Present-day erosion rates: Model input vs. observation input 10/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Simulation with model data Simulation with observational data
  • 12. Summary 11/28 1. How can we model local scale soil erosion on the global scale? • The adjusted RUSLE model reproduces present-day soil erosion rates for Europe and the USA 2. Can the global soil erosion rates be reproduced with data from ESMs? • Soil erosion rates derived from observational data can be reproduced using CMIP5 data, however, there is some uncertainty INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS I made the RUSLE model applicable on a coarse resolution on the global scale, however, the model is very sensitive to the climate and land cover data from ESMs Conclusion
  • 13. Modelling sediment dynamics on a global scale 12/28 Objective To develop a global model for sediment dynamics to quantify long-term changes in sediment fluxes Research Questions 1. How can we model long-term large-scale sediment dynamics? 2. How did sediment storage change during the last millennium and what were the main drivers? INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
  • 14. The new sediment budget model 13/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Flow routing scheme Naipal et al., 2015 (Esurf, under revision) Erosion (E(t)) = S * R * C * K Ma(t+1) = Ma(t) + deposition fraction( fa(t+1) ) * E(t+1) – Loss ( L(t) ) L (t) = Ma(t) / residence time (τ) Mc(t+1) = Mc(t) + deposition fraction( fc(t+1) ) * E(t+1)
  • 15. Experimental setup for simulating sediment budgets during the last millennium (850 – 2005 AD) 14/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Naipal et al., 2015 (Esurf, under revision)  Case studies: • Rhine catchment • Global  Climate and land cover/use data from MPI-ESM-LR (last millennium + historical experiments)  Equilibrium simulation with mean climate and landcover conditions from 850-950 AD  Transient simulations: 1. CC+LUC: Climate and land use change 2. CC: Climate change only (land use from 850AD) 3. LUC: Land use change only (climate from 850AD)  Change in sediment storage during the transient simulation
  • 16. The Rhine catchment 15/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Naipal et al., 2015 (Esurf, under revision)
  • 17. Rhine catchment validation: Scaling behavior 16/28 𝐷𝑎𝑡𝑎: 𝑆𝑡𝑜𝑟𝑎𝑔𝑒~𝐵𝑎𝑠𝑖𝑛 𝑎𝑟𝑒𝑎1.23±0.06 𝐷𝑎𝑡𝑎: 𝑆𝑡𝑜𝑟𝑎𝑔𝑒~𝐵𝑎𝑠𝑖𝑛 𝑎𝑟𝑒𝑎1.06±0.07 For floodplains: For hillslopes: INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Naipal et al., 2015 (Esurf, under revision) 𝑀𝑜𝑑𝑒𝑙: 𝑆𝑡𝑜𝑟𝑎𝑔𝑒~𝐵𝑎𝑠𝑖𝑛 𝑎𝑟𝑒𝑎1.2±0.04 𝑀𝑜𝑑𝑒𝑙: 𝑆𝑡𝑜𝑟𝑎𝑔𝑒~𝐵𝑎𝑠𝑖𝑛 𝑎𝑟𝑒𝑎1.05±0.06
  • 18. Rhine catchment validation: Millennial sediment storage 17/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Observations versus model for Rhine sub-catchments Naipal et al., 2015 (Esurf, under revision) 1:1 line trend line rmse=3.58
  • 19. Global: Millennial sediment storage 18/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
  • 20. Global: Most sediment stored on hillslopes 19/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
  • 21. Global validation: Modelled vs. observed sediment yield 20/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS trend line 1:1 line * Observed yields from Land2Sea database Peuker-Ehrenbrink (2009) rmse= 252
  • 22. Global: Land use as the main contributor to sediment fluxes 21/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Simulation I CC + LUC ΔM = 6526 Gt Simulation II CC ΔM = 5483 Gt ΔM = 6658 Gt Simulation III LUC Ganges Amazon Yellow Nile Mississippi
  • 23. Summary 22/28 1. How can we model long-term large-scale sediment dynamics? • The new sediment budget model reproduces the sediment storage change in the Rhine catchment and sediment yields globally 2. How did sediment storage change during the last millennium and what were the main drivers? • Sediment storage increased significantly during the last millennium for different global catchments, mainly due to land use change INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS Conclusion I developed a globally applicable sediment budget model, which shows that land use change is the main driver behind the change in sediment storage during the last millennium
  • 24. Laterally displaced carbon and nutrients 23/28 Objective To estimate the effect of soil erosion on the lateral fluxes of carbon and nutrients Research Questions 1. How large are present-day lateral fluxes of carbon and nutrients due to soil erosion only ? 2. How much of the eroded carbon and nutrients is exported by rivers? INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS
  • 25. Present-day eroded soil organic carbon (SOC) 24/28 SOC erosion rate (Esoc) = E * area-weighted SOC% INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS g m-2 y-1 Esoc flux: 5.1 Pg C y-1  Esoc emissions: 1.0 Pg C y-1 ~ 13% of fossil fuel emissions: 7.8 Pg C y-1  River flux: 3% of Esoc
  • 26. g m-2 y-1 Present-day eroded nitrogen 25/28 N erosion rate (En) = E * area-weighted N% INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS En flux: 336 Tg N y-1 ~ fertilizer use + fixation + deposition: 341 Tg N y-1  River flux: 4% of En
  • 27. Present-day eroded phosphorus 26/28 P erosion rate (Ep) = E * area-weighted P% INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS g m-2 y-1 Ep flux: 94 Tg P y-1 > fertilizer use + weathering: 50 Tg P y-1  River flux: 7% of Ep
  • 28. Summary 27/28 1. How large are present-day lateral fluxes of carbon and nutrients due to soil erosion only ? • Soil erosion results in significant fluxes of carbon and nutrients globally 2. How much of the eroded carbon and nutrients is exported by rivers? • Only a small part of the mobilized carbon and nutrients is exported by rivers INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS I show that soil erosion and associated sediment dynamics should not be neglected in studying the global biogeochemical cycles Conclusion
  • 29.  I developed the first dynamical global sediment budget model that reproduces the global features of sediment dynamics  I show that the effects of soil erosion and associated sediment dynamics on the biogeochemical cycles are globally significant and should not be neglected Overall Conclusions 28/28 INTRODUCTION SOIL EROSION SOIL REDISTRIBUTION CARBON & NUTRIENTS CONCLUSIONS  Implementing the sediment budget model in MPI-ESM and other ESMs  Coupling the sediment budget model with the biogeochemical components of ESMs  Include other types of soil erosion: landslides, gullying, glacial erosion Outlook