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Process-based modeling
in alpine catchments
Giacomo Bertoldi, Stefano Della Chiesa, Michael Engel, Georg Niedrist, Johannes G. Brenner , 
Stefano Endrizzi, Matteo Dall’Amico, Emanuele Cordano, Ulrike Tappeiner, Riccardo Rigon. 
EGU 2014, Vienna, Austria, 28 April – 2 May 2014
Institute for Alpine    
Environment
Aims and outline
Motivation
In mountain regions ecohydrological processes exhibit rapid changes within short 
distances due to the complex interplay of topography, soil, biological and 
atmospheric processes. 
Are process‐based models able to deal with this complexity?
Outline
An (hopefully) useful instrument: the GEOtop 2 ‐ DV model.
Application of the model to mountain areas:
1. Plot scale
Modelling snow, soil moisture, ET, biomass  along an elevation gradient:
Model as a tool to investigate coupled eco‐hydrological processes.
2. Catchment scale
Remote sensing land surface temperature in complex terrain:
Model as tool  to interpret processes behind observations 
Discuss advantages and constraints of process based modelling in mountain areas
Coupled process based modelling in mountain areas 
LWatm

V
D0VI
LWsurr

1V 
SWsurr

1V 
sTs
4
Shortwave
radiation (yellow)
Longwaveradiation
(red)
SWrefl
Complex topography
Bertoldi et al., J of Hydromet, 2006.
s
Snow module
Endrizzi et al., GMDD, 2014
Zanotti et al., Hydrol Proc, 2004
Water budget
Rigon et al., J of Hydromet, 2006.
Figures adapted from VIC model (Liang et al., 1994)
Energy budget
Bertoldi al., Ecohydrol, 2010.
Vegetation dynamics
Della Chiesa et al., Ecohydrol., 2014
From SHE model (Abbot et al., 1986)
The GEOtop 2.0  – DV  model
Rigon et al., JHM, 2006; 
Endrizzi et al. GMDD, 2014.
Processes
Dynamic vegetation
model (for grasslands)
From Montaldo et al.,  2005;
Della Chiesa et al., 2014
Does it works?
Is  it usable ?      Or … too complex?
Is it useful ?
Two applications in mountain context
1. Plot scale
Modelling snow, soil moisture, ET, biomass  along an elevation gradient:
Model as a tool to investigate coupled eco‐hydrological processes.
2. Catchment scale
Remote sensing land surface temperature in complex terrain:
Model as tool  to interpret processes behind observations.
Application 1: modelling along an elevation gradient
Motivation
In dry inner‐alpine regions, managed grasslands are irrigated.
Climate change raises issues about future water availability.
Which are the effects of the elevation gradient on SWE, SWC, ET,
grassland productivity?
Della Chiesa et al., Modeling changes in grassland  hydrological cycling 
along an elevational gradient in the Alps,
Ecohydrology, 2014
.
An experimental elevation transect
Elevation as a proxy of climate change: Mazia Valley, emerging LTER
Station 
B2000 m
Hs, SWC, 
Biomass, GAI
Station
B1500 m
Hs, SWC, 
Biomass, GAI,ET
Station
B1000 m
Hs, SWC, 
Biomass, GAI
T~ 3.5K
T~ 3.5K
Elevation gradient: validation
Multiple variables validation: SWE, SWC, above ground biomass (Bag), ET
Two years of data: calibration in B1500, validation in B1000, B2000
B2000 mB1500 mB1000 m
Snow Height [cm] SWC 5cm [] ET [mm]
Not Measured
Not Measured
r2=0.66
RMSE=7.1
r2=0.57
RMSE=5.9
r2=0.55
RMSE=2.9
r2=0.80
r2=0.78
r2=0.82
Bag [gDMm‐2]
RMSE=0.04
RMSE=0.05
RMSE=0.04
r2=0.93
RMSE=58.39
Elevation gradient: resultsB2000 mB1500 mB1000 m
Simulation extension to 20 year 
Coupling snow – veg – ET ‐ SWC Water limitation below 1500 m
SWC along the year
Elevation gradient: resultsB2000 mB1500 mB1000 m
Coupling snow – veg – ET ‐ SWC
SWC along the year
Irrigation below 1500 m
Application 1: modelling along an elevation transect
Insight on process understanding
In the Vinschgau valley, water limits ET below an elevation threshold of 1500 m a.s.l. 
while, above, the temperature and vegetation period length act as limiting factor. 
Modelling lesson learning
Need of coupled modelling 
of energy and water fluxes, snow and vegetation dynamic.
Model validation against multiple variables
adds additional constrains to model consistency.
SWE     →     SWC
↕
Bag ↔ LAI ↔ ET
Application 2: land surface temperature
Motivation
LST is a key variable of the surface energy budget.
Improving its estimation in energy budget models can improve fluxes partitioning estimation.
Which are the factors controlling LST in mountain environments
(i.e. elevation, solar radiation, land cover, soil moisture)?
Bertoldi et al., Topographical and ecohydrological controls
on land surface temperature in an Alpine catchment, 
Ecohydrology, 3, 189 – 204, 2010.   
t
E
wLSTETLSTHwLSTGLSTR ssn


 ),()(),()( 4
Modeling land surface temperature
Stubai Valley experimental area (Tyrol, Austria)
(Institute of Ecology Innsbruck University)
•257 km2, elevation 1000 ‐ 3500 m.
• Humid inner‐alpine climate. 
• Comparison with 60 m LANDSAT LST TIR ETM+ map (13 
September 1999, 10.50 AM).
• Parameters from field data (Hammerle et al. 2007) and 
literature for different land cover types (Findell et al. 
2007).
• One year model spin‐up to reach equilibrium.
• Model validation against ground observations.
• Leaf Area Index (LAI);  Roughness length (z0).
LST: spatial patterns comparison
Aspect R2=0.63
Numerical experiment:
add only one spatially varying factor at a time
LST: spatial patterns comparison
Aspect R2=0.63
Elevation R2=0.74
LST: spatial patterns comparison
Aspect R2=0.63
Elevation R2=0.74
Land cover R2=0.88
LST: spatial patterns comparison
The model helps to identify factors controlling LST patterns 
Aspect R2=0.63
Elevation R2=0.74
Land cover R2=0.88
Moisture R2=0.89
Application 2: land surface temperature
Insight on process understanding
Most relevant factors controlling LST result radiation distribution and elevation.
Alpine vegetation and aspect strongly alter LST vertical distribution.
Modelling lesson learning
Need to have a model with LST as explicit prognostic variable.
Model helps to discriminate controlling factors.
(Complex) model allows to simplify complex patterns.
Benefits (and issues) from process based modeling ?
Issues
“Distributed model are 
overparameterized”.
“ Such a models cannot be really 
calibrated”.
“They cannot be used for unequipped 
basins”.
“Reality is simpler than that (and we 
learn just from simple models)”.
From “analogic” ….
Possible solutions
Coupling processes introduces 
additional constrains.
Use multiple/ multi‐scale observations. 
Tools to extend detailed experimental 
campaigns.
Numerical experiments allow to 
discriminate controlling factors.
Toward “digital”?
GEOtop is an Open Source collaborative project and
others are invited to bring into new components.
https://code.google.com/p/geotop/
Main model developers: 
Università di Trento; Zurich University (Now Quebec University);
Mountain‐eering S.r.l; EURAC research; University of Augsburg KIT.
Creating a community. Try it!
Acknowledgments
This study is supported by the projects “HiResAlp” and “HydroAlp” financed by Provincia 
Autonoma di Bolzano, Alto Adige, Ripartizione Diritto allo sudio, Università e ricerca scientifica.
The RADARSAT2 images were made available through the project ESA AO 6820 in the 
framework of the SOAR program.
• We hereby would like to thank:
C. Notarnicola, EURAC, Institute for Alpine Environment.  
Thank you for your attention!
Application 3: remote sensing of soil moisture
Motivation
Limited availability of reliable soil moisture high resolution products on mountain areas. 
Heterogeneity in soil type, land cover,  topography limits distributed models parameterization.
How far can SAR remote sensing help for improving modelling surface soil moisture 
in mountain grassland areas?
Bertoldi, G., et al. Estimation of soil moisture patterns
in mountain grasslands by means of
SAR RADARSAT2 images and 
hydrological modeling. J. Hydrol. (2014)
RADASAT2 SAR 
Soil moisture: observations
Fixed Stations
Field surveys
Mazia, South 
Tyrol, Italy ~ 
100 km2
RADASAT2 SAR 
images 20m res
Surface SWC 
retrieval (SVR Pasolli 
et el., 2011)
Soil moisture: spatial patterns comparison
SWC  SWC 
Soil moisture: spatial patterns comparison
Insight on process understanding
Model suggest that soil type and land management are major controls on  surface SWC.
Modelling lesson learning
Limitation in model performance  due coarse soil type / land cover information available.
SAR remote sensing is able to provide higher spatial resolution information.
Use RS information for model parameterization / data integration/ assimilation. 
SWC  SWC 
EGU 2014 invited talk (mostly on simulation of ecohydrology) - by Giacomo Bertoldi et al

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