Atmos. Chem. Phys., 11, 7781–7816, 2011
www.atmos-chem-phys.net/11/7781/2011/
doi:10.5194/acp-11-7781-2011
© Author(s) 2011. CC Attribution 3.0 License.
Atmospheric
Chemistry
and Physics
Global dust model intercomparison in AeroCom phase I
N. Huneeus1 , M. Schulz1,2 , Y. Balkanski1 , J. Griesfeller1,2 , J. Prospero3 , S. Kinne4 , S. Bauer5,6 , O. Boucher8,* ,
M. Chin9 , F. Dentener10 , T. Diehl11,12 , R. Easter13 , D. Fillmore14 , S. Ghan13 , P. Ginoux15 , A. Grini16,17 , L. Horowitz15 ,
D. Koch5,6,7 , M. C. Krol18,19 , W. Landing20 , X. Liu13,21 , N. Mahowald22 , R. Miller6,23 , J.-J. Morcrette24 , G. Myhre16,25 ,
J. Penner21 , J. Perlwitz6,23 , P. Stier26 , T. Takemura27 , and C. S. Zender28
1 Laboratoire
des Sciences du Climat et de l’Environnement, CEA-CNRS-UVSQ, IPSL, Gif-sur-Yvette, France
Institut, Oslo, Norway
3 Rosenstiel School of Marine and Atmospheric Science, University of Miami, Miami, FL., USA
4 Max-Planck-Institut für Meteorologie, Hamburg, Germany
5 The Earth Institute, Columbia University, New York, USA
6 NASA Goddard Institute for Space Studies, New York, NY, USA
7 US Department of Energy, Washington, DC, USA
8 Met Office, Hadley Centre, Exeter, UK
9 NASA Goddard Space Flight Center, Greenbelt, MD, USA
10 European Comission, Joint Research Centre, Institute for Environment and Sustainability, Italy
11 NASA Goddard Space Flight Center, Greenbelt, Maryland, USA
12 Universities Space Research Association, Columbia, Maryland, USA
13 Pacific Northwest National Laboratory, Richland, WA, USA
14 NCAR, Boulder, Colorado, USA
15 NOAA, Geophysical Fluid Dynamics Laboratory, Princeton, New Jersey, USA
16 Department of Geosciences, University of Oslo, Oslo, Norway
17 Kongsberg Oil & Gas Technologies, Norway
18 Utrecht University, Institute for Marine and Atmospheric Research, Utrecht, The Netherlands
19 Wageningen University, Meteorology and Air Quality, Wageningen, The Netherlands
20 Departement of Earth, Ocean and Atmospheric Science, Florida State University, Tallahassee, FL, USA
21 Department of Atmospheric, Oceanic and Space Sciences, University of Michigan, Ann Arbor, MI, USA
22 Departement of Earth and Atmospheric Sciences, Cornell University, Ithaca, New York, USA
23 Department of Applied Physics and Applied Mathematics, Columbia University, New York, USA
24 European Centre for Medium-Range Weather Forecasts, Reading, UK
25 Center for International Climate and Environmental Research – Oslo (CICERO) Oslo, Norway
26 Atmospheric, Oceanic and Planetary Physics, Department of Physics, University of Oxford, UK
27 Research Institute for Applied Mechanics, Kyushu University, Fukuoka, Japan
28 Department of Earth System Science, University of California, Irvine, USA
* now at: Laboratoire de Météorologie Dynamique, IPSL, CNRS/UPMC, Paris, France
2 Meteorological
Received: 5 August 2010 – Published in Atmos. Chem. Phys. Discuss.: 12 October 2010
Revised: 29 June 2011 – Accepted: 9 July 2011 – Published: 3 August 2011
Abstract. This study presents the results of a broad intercomparison of a total of 15 global aerosol models within the
AeroCom project. Each model is compared to observations
related to desert dust aerosols, their direct radiative effect,
and their impact on the biogeochemical cycle, i.e., aerosol
optical depth (AOD) and dust deposition. Additional comCorrespondence to: N. Huneeus
(
[email protected])
parisons to Angström exponent (AE), coarse mode AOD and
dust surface concentrations are included to extend the assessment of model performance and to identify common biases
present in models. These data comprise a benchmark dataset
that is proposed for model inspection and future dust model
development. There are large differences among the global
models that simulate the dust cycle and its impact on climate.
In general, models simulate the climatology of vertically integrated parameters (AOD and AE) within a factor of two
Published by Copernicus Publications on behalf of the European Geosciences Union.
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
whereas the total deposition and surface concentration are
reproduced within a factor of 10. In addition, smaller mean
normalized bias and root mean square errors are obtained
for the climatology of AOD and AE than for total deposition and surface concentration. Characteristics of the datasets
used and their uncertainties may influence these differences.
Large uncertainties still exist with respect to the deposition
fluxes in the southern oceans. Further measurements and
model studies are necessary to assess the general model performance to reproduce dust deposition in ocean regions sensible to iron contributions. Models overestimate the wet deposition in regions dominated by dry deposition. They generally simulate more realistic surface concentration at stations
downwind of the main sources than at remote ones. Most
models simulate the gradient in AOD and AE between the
different dusty regions. However the seasonality and magnitude of both variables is better simulated at African stations than Middle East ones. The models simulate the offshore transport of West Africa throughout the year but they
overestimate the AOD and they transport too fine particles.
The models also reproduce the dust transport across the Atlantic in the summer in terms of both AOD and AE but not so
well in winter-spring nor the southward displacement of the
dust cloud that is responsible of the dust transport into South
America. Based on the dependency of AOD on aerosol burden and size distribution we use model bias with respect to
AOD and AE to infer the bias of the dust emissions in Africa
and the Middle East. According to this analysis we suggest
that a range of possible emissions for North Africa is 400 to
2200 Tg yr−1 and in the Middle East 26 to 526 Tg yr−1 .
1
Introduction
Desert dust plays an important role in the climate system.
Models suggest that dust is one of the main contributors to
the global aerosol burden (Textor et al., 2006) and has a
large impact on Earth’s radiative budget due to the absorption, scattering and emissions of solar and infrared radiation
(Sokolik et al., 2001; Tegen, 2003; Balkanski et al., 2007).
The deposition of desert dust to the ocean is an important
source of iron in high-nutrient-low-chlorophyll (HNLC) regions (Mahowald et al., 2009). This iron contribution may
be crucial for the ocean uptake of atmospheric CO2 through
its role as an important nutrient for phytoplankton growth
(Jickells et al., 2005; Aumont et al., 2008; Tagliabue et al.,
2009). Dust also plays a significant role in tropospheric
chemistry mainly through heterogeneous uptake of reactive
gases such as nitric acid (Bian and Zender, 2003; Liao et
al., 2003; Bauer et al., 2004) and heterogeneous reactions
with sulfur dioxide (Bauer and Koch, 2005). Furthermore,
mineral aerosols are important for air quality assessments
through their impact on visibility and concentration levels
of particulate matter (Kim et al., 2001; Ozer et al., 2007;
Atmos. Chem. Phys., 11, 7781–7816, 2011
Jimenez-Guerrero et al., 2008). Links between the occurrence of meningitis epidemics in Africa and dust have been
suggested (Thomson et al., 2006). Impacts on climate and air
quality are intimately coupled (Denman et al., 2007).
Many global models simulate dust emissions, its transport
and deposition in a coherent manner (e.g. Guelle et al., 2000;
Reddy et al., 2005b; Ginoux et al., 2001; Woodage et al.,
2010). A large diversity has been documented between models in terms of e.g. dust burden and aerosol optical depth introducing uncertainties in estimating the direct radiative effect, and even more difficult the anthropogenic component
of it (Zender et al., 2004; Textor et al., 2006; Forster et al.,
2007). On the other hand, inter-model differences in simulated dust emission and deposition fluxes make estimating
the impact of dust on ocean CO2 uptake in HNLC regions
difficult (Textor et al., 2006; Tagliabue et al., 2009).
An exhaustive comparison of different models with each
other and against observations can reveal weaknesses of individual models and provide an assessment of uncertainties
in simulating the dust cycle. Uno et al. (2006) compared
multiple regional dust models over Asia in connection to
specific dust events. They concluded that even though all
models were able to predict the onset and ending of a dust
event and were able to reproduce surface measurements,
large differences existed among them in processes such as
emissions, transport and deposition. Todd et al. (2008) conducted an intercomparison with five regional models for a
3-day dust event over the Bodélé depression. The analyzed
model quantities presented a similar degree of uncertainty
as reported by Uno et al. (2006). Kinne et al. (2003) compared aerosol properties from seven global models to satellite and ground data. The largest differences among models
were found near expected source regions of biomass burning
and dust. Further global model intercomparisons have been
conducted within the AeroCom project (http://nansen.ipsl.
jussieu.fr/AEROCOM/). Textor et al. (2006) conducted an
intercomparison between global models of the life cycle of
the main aerosol species. Large differences (diversity) were
found in emissions, sinks, burdens and spatial distribution
for the different aerosol species simulated. These diversities reveal uncertainties in simulating aerosol processes that
have large consequences for estimating the radiative impact
of dust. However, no comparisons against observations were
made in that study. Kinne et al. (2006) extended the study
of Kinne et al. (2003) and compared the aerosol properties
from all AeroCom models to satellite and ground data. None
of these AeroCom studies however, focused exclusively on
dust particles. Tegen (2003) compared the dust cycle simulated by two global dust models to satellite climatology of
TOMS aerosol index (AI). Zender et al. (2004) compared the
emission fluxes and burdens for different models. Prospero
et al. (2010) conducted a more exhaustive intercomparison,
comparing and evaluating the temporal and spatial variability of African dust deposition in Florida simulated by models
within the AeroCom initiative. The comparison shows that in
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
general models reproduce the seasonal variability but most
yield weak summer maxima.
This work represents a broader dust model intercomparison. Global dust models within AeroCom are compared
against each other and against different datasets. By using
one homogeneous model data compilation (model versions
in AeroCom and documented by Textor et al., 2006) we
demonstrate the use of a benchmark data test set for across
model inspections and for future developments of dust models. We compare each model to observations focusing on
variables related to the uncertainties in the estimation of the
direct radiative effect and the dust impact on the ocean biogeochemical cycle, i.e. aerosol optical properties and dust
deposition as well as surface concentration. The article is
structured as follows. We start by describing the data used
in the validation and the different models considered in this
work (Sect. 2). The results are presented in Sect. 3 while
the discussion of these results is given in Sect. 4. Finally in
Sect. 5 the conclusions of this work are presented.
2
Data and models
We evaluate the models described in Sect. 2.4 against insitu measurements of dust deposition (Sect. 2.1) and surface
concentration (Sect. 2.2) as well as retrievals of aerosol optical depth (AOD, Sect. 2.3) and Angström exponent (AE,
Sect. 2.3). A brief description of each of these datasets follows together with a brief description of the AeroCom models used in this work.
2.1
Dust deposition
Deposition at sites remote from sources serves as a powerful
constraint on the overall global dust budget. Total deposition
fluxes are most useful when accumulated over long time periods. In this way direct dust deposition data have been used
in the validation of global dust models.
We first use three compilations giving deposition fluxes
over land. We use the measured deposition fluxes given in
Ginoux et al. (2001) based partly upon measurements taken
during the SEAREX campaign (Prospero et al., 1989; capital letters in Fig. 1). Only those data corresponding to actual measurements were considered. Most sites are located
in the Northern Hemisphere and far away from source regions. The measured values range from 450 [g m−2 yr−1 ]
in the Taklimakan desert to 0.09 [g m−2 yr−1 ] in the equatorial Pacific; measurement periods vary according to the site.
Mahowald et al. (2009) present a compilation with a total of
28 sites measuring iron and/or dust deposition, mostly in the
last two decades (non-italic numbers in Fig. 1). We assume a
3.5 % iron content in dust to infer dust deposition fluxes from
iron deposition. This value is the average iron content of the
Earth’s crust and is widely used in studies deriving iron inputs to the ocean from dust aerosols (Mahowald et al., 2005;
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Hand et al., 2004). The iron content in soils varies according to the source region but studies suggest that uncertainties
in dust deposition and iron solubility are more important to
understand than the variability of iron content in different
source regions (Mahowald et al., 2005). In addition we use
deposition fluxes derived from ice core data (lower case letters in Fig. 1). These depositions have proven to be accurate
to represent the current climate (Mahowald et al., 1999).
We then use deposition fluxes measured from sediment
traps and collected in the Dust Indicators and Records
in Terrestrial and Marine Paleoenvironments (DIRTMAP)
database (Tegen et al., 2002; Kohfeld and Harrison, 2001;
italic numbers in Fig. 1). We follow Tegen et al. (2002) and
only use those stations with deployment period larger than
50 days and sites without contamination from suspected fluvial inputs or hemipelagic reworking. This database contains
a set of comparable deposition fluxes providing a picture of
the gradients in the intensity of the dust deposition to the Atlantic Ocean and the Arabian Sea. In addition, we also follow Tegen et al. (2002) and Mahowald et al. (2009) and do
not use DIRTMAP deposition data derived from marine sediment cores because they represent the integrated dust flux to
the ocean over a time span of hundreds to possibly thousands
of years and are thus inadequate to be used in the evaluation
of simulation of the dust cycle for specific years (Tegen et
al., 2002).
The total deposition data used in this study comes from
84 sites with yearly dust deposition fluxes that are not coincident in time with the model simulated year (Table S1 in
the Supplement). Model yearly deposition fluxes were computed using all days. Except for the ice core data, the sites
have been grouped regionally. To facilitate the comparison
with model data, each of these regions is identified with a
different colour in Fig. 1. Given the characteristics described
above, we suggest that these datasets represent to first order a
modern or present-day climatology of dust deposition observations. However, some of these measurements do not cover
a sufficiently long period to qualify as “climatological” in
a strict sense. The impact of this assumption on the model
evaluation will be considered in the discussion (Sect. 4). Deposition data from the same locations were averaged in order
to provide one climatological data set.
Dust particles are efficiently removed by wet scavenging,
especially over the open ocean (Prospero et al., 2010; Hand et
al., 2004; Gao et al., 2003). To test the wet deposition simulated by the models we compare simulated deposition against
data from the Florida Atmospheric Mercury Study (FAMS)
network (Prospero et al., 2010) and from a compilation of
estimates of the fraction of wet deposition (Mahowald et al.,
2011). For the former a total of nine stations measured wet
and total deposition during almost three years (April 1994 till
end of 1996). These data have already been used to evaluate
some AeroCom models in Prospero et al. (2010). Nevertheless, we include this dataset to extend the comparison to the
expanded set of AeroCom models.
Atmos. Chem. Phys., 11, 7781–7816, 2011
Measured yearly deposition fluxes versus modeled ones; units are g m−2 yr−1 . Location for each data point in the scatter plot is given in the upper left subfigure. Number and letters are coloured regionally for West/East Pacific
Data from Ginoux et al. (2001)/Mahowald et al. (2009)/DIRTMAP/Mahowald et al. (1999) are indicated by letters/non-italic numbers/italic numbers/lower-case letters. Root mean square error (RMS), bias, ratio of modeled and observed
7784
standard deviation (sigma) and correlation (R ) are indicated for each model in the lower right part of the scatterplot. Mean normalized bias and normalized root mean square error are given in parenthesis next to RMS and mean bias,
respectively. The correlation with respect to the logarithm of the model and of the observation is also given in parenthesis next to R . Black continuous line is the 1:1 line whereas the black dotted lines correspond to the 10:1 and 1:10
lines. Names and locations for each selected station are given in Table S1 in the Supplement.
Atmos. Chem. Phys., 11, 7781–7816, 2011
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
Fig. 1.
(red/brown), North/Tropical/South Atlantic (orange/black/light-blue), Middle East/Asia/Europe (violet/purple/light green), Indian/Southern Ocean (dark green/dark blue) and pink ice core data in Greenland, South America and Antartica.
N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
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In general the cut-off size of the deposition measurements
is not provided in model evaluation studies and is difficult to
find. This cut-off size depends on the instrument used and
it can be as high as several tenths of micrometers (Goossens
and Rajot, 2008). No size distribution data of the deposited
dust for the period of measurements are provided. However Reid et al. (2003) and Li-Jones and Prospero (1998)
reported measurement diameters of Saharan dust particles
mainly smaller than 10 µm across the Atlantic Ocean on the
eastern limit of the Caribbean Sea. Since most of our deposition data corresponds to measurements in remote regions and
most models only simulate dust particles up to 10 µm, we do
not consider the cut-off size as a significant source of bias in
the results.
2.2
Surface concentration
Surface concentrations are an alternative mean to evaluate
the transport and dispersion of simulated dust. We compare the AeroCom models with monthly dust concentration
measurements taken at 20 sites managed by the Rosenstiel
School of Marine and Atmospheric Science at the University
of Miami (Prospero et al., 1989; Prospero, 1996; Arimoto
et al., 1995). The measurements taken in the Pacific Ocean
are from the sea/air exchange (SEAREX) program (Prospero
et al., 1989) whereas the measurements from the northern
Atlantic are from the Atmosphere-Ocean chemistry experiment (AEROCE, Arimoto et al., 1995). Both experiments
were designed to study the large-scale spatial and temporal
variability of aerosols. Most measuring sites are located far
downwind of dust emission sources (Fig. 2). A list of the
stations and their location is given in Table S2 in the Supplement. The dust concentrations are derived from measured
aluminium concentrations assuming an Al content of 8 %
in soil dust (Prospero, 1999) or from the weights of filter
samples ashed at 500 ◦ C after extracting soluble components
with water. This database has been largely used for the evaluation of dust models (e.g. Ginoux et al., 2001; Cheng et
al., 2008; Tegen et al., 2002) and in the reports of the Intergovernmental Panel of Climate Change (IPCC) of 2001 and
2007. The measurements were taken for the most part in the
1980s and 1990s with varying measurement periods at each
station. We extend this data set with monthly dust concentrations at Rukomechi, Zimbabwe (Maenhaut et al., 2000a;
Nyanganyura et al., 2007) and Jabiru, Australia (Maenhaut
et al., 2000b; Vanderzalm et al., 2003). The primary goal
of these measurements was to study aerosol composition in
Rukomechi and the impact of biomass burning in northern
Australia. Nevertheless, we include these data because dust
was one of the species measured during these long term measurements.
We have separated the sites in three distinctive groups according to the range of measured data. The first group corresponds to stations with monthly mean surface concentrations
lower than 1 µg m−3 throughout the year (LOW). These stawww.atmos-chem-phys.net/11/7781/2011/
Fig. 2. Network of stations measuring surface concentration
(Sect. 2.2). Stations are grouped according to the regime of measured data into remote stations (orange), stations under the influence
of minor dust sources of the Southern Hemisphere or remote sites
in the Northern Hemisphere (violet) and finally locations directly
downwind of African and Asian dust source (blue). Stations within
each group are numbered from south to north. Names and locations
for each selected station are given in Table S2 in the Supplement.
Rectangles illustrate regions defined to compute the emissions presented in Table 5.
tions are located in the Antarctica and in the Pacific Ocean
below 20◦ N far from any dust sources. Orange numbers
and dots illustrate them in Fig. 2. The second group (in violet in Fig. 2) corresponds to stations under the influence of
minor dust sources of the Southern Hemisphere or remote
sites in the Northern Hemisphere (MEDIUM). Finally, the
third group corresponds to locations downwind of African
and Asian dust sources, presented by blue numbers and dots
in Fig. 2 (HIGH). In each of these groups the stations are ordered from south to north. A list of the stations with their
location, identifier used in Fig. 2 and attributed data range
group is given in Table S2 of the Supplement. The simulated
monthly averages of surface concentrations for all models are
computed using all days.
In addition, we complement the monthly averages with the
data set of surface concentrations presented in Mahowald et
al. (2009). These data correspond to measurements taken
mostly during cruises but include also long term measuring
stations. The measurements taken during cruise campaigns
will be compared to yearly averages even though they represent short-term data. Mahowald et al. (2009) show that
30–90 % of the annually averaged deposited dust is seen on a
few days (5 %). In order to account for the error of comparing model yearly averaged surface concentration with shortterm measurements we follow Mahowald et al. (2008) and
show the range of values representing the median 66 % of
the daily averaged model concentration as an error bar on the
model and annual mean (vertical dashed line) for each cruise
data. Because the long-range transport of dust is an important
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
attribute and we do not have monthly mean values at many
locations, we include this cruise data with large uncertainty
bars until better data is available.
We consider all the above described data sets as “climatology” even though they do not cover a long enough period to
be termed climatology in a strict sense.
We also use measurements from the year 2000 at Barbados
station and at Miami consistent with the model output from
the AeroCom models used in this study and presented below (Sect. 2.4). This is the most extensive long-term record
of surface dust concentration available. Concentrations have
been measured under on-shore wind conditions almost continuously since 1965 in an equivalent manner as described
above (Prospero, 1999; Prospero and Lamb, 2003). The Barbados data have been used to study the long-range transport
from African dust over the Atlantic and the factors influencing its variability (Prospero and Nees, 1986; Prospero and
Lamb, 2003; Chiapello et al., 2005). We will compare these
measurements to the climatological cycle described above
and evaluate how representative the climatology is from the
year 2000.
The instruments used to measure surface concentrations
efficiently captured particles below 40 µm in stations managed by the Rosenstiel School of Marine and Atmospheric
Science at the University of Miami. While this cut-off limit
could be critical for model evaluation close to sources (provided coarse dust particles are present) it is safe to assume
that it is less important in remote stations. Measurements
on the eastern limit of the Caribbean Sea reported diameters
of Saharan dust particles mainly smaller than 10 µm (Reid et
al., 2003; Li-Jones and Prospero, 1998). Furthermore most
models considered in this study only simulate dust particles
up to 10 µm.
2.3
Aerosol optical depth and Angström exponent
The widespread deployment of sun photometers in the last
ten years has provided very reliable global information about
dust, although limited to times when dust dominates the
AOD. When full inversions of multiple-angle sky observations are available, coarse mode AOD may provide a better
estimate of dust optical depth. Note that the measurements
are biased towards daytime, clear-sky conditions. AOD retrievals may also miss very dusty situations because of cloud
discrimination problems. The AErosol RObotic NETwork
(AERONET) is a global network of photometers that delivers
numerical data to monitor and characterize the aerosols in a
regional and/or global scale. The network has more than 300
stations distributed in the world measuring aerosol in both
remote and polluted areas (Holben et al., 1998, 2001). We
use here AERONET total AOD and coarse mode AOD at
550 nm and Angström exponent (AE). Typically, the uncertainty in AOD under cloud-free conditions is of 0.01 at 550
and 865 nm and 0.02 at 440 nm (Holben et al., 1998). The
coarse mode AOD requires almucantar and azimuth plane
Atmos. Chem. Phys., 11, 7781–7816, 2011
measurements; these requirements limit the amount of data
since these scans cannot be accomplished nearly so regularly
as the direct sun radiances which also allow the retrieval of
the total AOD. The AE is calculated from multi-wavelength
direct sun observations and delivers useful information on
the aerosol size distribution. The simulated AE is computed
from the estimated AOD at 550 and 865 nm whenever the
model does not provide it.
Although AERONET provides daily averaged data of the
above mentioned parameters we focus solely on the monthly
mean. This provides a comprehensive picture of the seasonal dust cycle but precludes the evaluation of the frequency
and intensity of dust events. The evaluation of the ability of
global dust models to simulate individual dust events is beyond the scope of this work. Model monthly averages are
constructed from daily means by selecting those days when
observations are available. Note that an overall average from
these monthly aggregates will be different than that of all
daily data. We use all available stations with measurements
for the year 2000 and a climatology constructed from the
multi-annual database 1996–2006.
The AERONET network has stations spread around the
world delivering aerosol data under various different atmospheric aerosol loads. In order to evaluate the models with
respect to dust only, we selected those stations dominated by
dust. We refer hereafter to these stations as “dusty” sites.
We use a selection method based upon Bellouin et al. (2005)
to differentiate between stations influenced by coarse, fine,
or a mixture of these aerosol modes. In contrast to the authors who used the accumulation-mode fraction to discern
between these three cases, we use the AE. We assume that
AERONET stations with AE smaller than 0.4 are dominated
by natural or coarse mode aerosols whereas those with values higher than 1.2 are dominated by anthropogenic or fine
mode aerosols. Stations with values within these boundaries
are exposed to a mixture of fine and coarse aerosols. Assuming that the AOD (at 440 nm) of oceanic aerosols does
not exceed 0.15 (Dubovik et al., 2002), we filter out the
oceanic aerosol stations from stations dominated by dust
aerosols by eliminating those stations with monthly AOD
(at 550 nm) smaller than 0.2. It should be noted that in remote stations fine mode desert dust can be mixed with other
fine mode aerosols (sulphate, black carbon, organic matter)
and thus have AE larger than 1.2. However, since we cannot separate these stations from those dominated by other
fine mode aerosols based only on AE, we base our filtering
criteria solely on the coarse mode. Therefore we define an
AERONET station as “dusty” if it has simultaneously at least
two months in the year (not necessarily consecutive) where
the monthly average AE is smaller than 0.4 and where the
monthly average of total AOD is larger than 0.2. We require
at least two months in order to avoid selecting sites where
a monthly average could be biased by a single day of low
AE not necessarily linked to desert dust. For comparisons
purpose however we consider all months with AE smaller
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Table 1. Description of the global models considered in this study. Aerocom Median is not included in this table since it is constructed
at every grid point and for every month by computing the local median from the models specified in Table 2. Models have been grouped
according to their size ranges; models CAM to UMI simulate dust aerosols in the size range 0.1–10 µm, models ECMWF and LOA in the
size range 0.03–20 µm and UIO CTM in the range 0.05–25 µm. Models LSCE, TM5, ECHAM5-HAM and MIRAGE describe dust aerosols
through 1, 2, 2 and 4 modes respectively.
N
Model
Resolution
Characteristics of size
distribution
Winds5
Emissions
Reference of emission
scheme
Model Reference
1
CAM
2.8◦ ×2.8◦ ×26 levels
4 bins
0.1–1–2.5–5–10 µm
Prescribed by
GCM
Interactived
Zender et al. (2003);
Mahowald et al.
(2006)
Mahowald et al.
(2006)
2
GISS
5◦ ×4◦ ×20 layers
4 bins
0.1–1–2–4–8 µm
NCEPb
reanalysis
Interactive
Cakmur et al. (2006)
Schmidt et al. (2006);
Bauer and Koch
(2005); Miller et al.
(2006)
3
GOCART
2◦ ×2.5◦ ×30 layers
5 bins1
0.1–1.0–1.8–3.0–6.0–
10.0
GEOS-3 DASc
Analysis
Interactive
Ginoux et al. (2001)
Chin et al. (2000)
4
SPRINTARS 1.125◦ ×1.125◦ ×20
layers
6 bins
0.1–0.22–0.46–1.0–
2.15–4.64–10.0
NCEPb
reanalysis
Interactived
Takemura et al.
(2009)
Takemura et al.
(2005)
5
MATCH
1.9◦ ×1.9◦ ×28 layers
4 bins
0.1–1.0–2.5–5.0–10
NCEPb
reanalysis
Interactived
Zender et al. (2003)
Zender et al. (2003)
6
MOZGN
1.9◦ ×1.9◦ ×28 layes
5 bins
0.1–1.0–1.8–3.0–6.0–
10.0
NCEPb
reanalysis
Interactived
Ginoux et al. (2001)
Horowitz et al.
(2003); Tie et al.
(2005)
7
UMI
2.5◦ ×2◦ ×30 layers
4 bins
0.05–0.63–1.25–2.5–
10 µm radius
NASA DAOa
reanalysis
Off-line
Ginoux et al. (2001)
Liu and Penner
(2002); Liu et al.
(2007)
8
ECMWF
0.7◦ ×0.7◦ ×60 levels
3 bins
0.03–0.55–0.9–20 µm
ECMWF
reanalysis
Interactived
Morcrette et al.
(2009)
Morcrette et al.
(2009)
9
LOA
3.75◦ ×2.5◦ ×19 layers
2 bins2
0.03–0.5–20 µm
ECMWF
reanalysis
Off-line
Balkanski et al.
(2004)
Reddy et al.
(2005a, b)
10
UIO CTM
2.8◦ ×2.8◦ ×40 layers
8 bins
0.03–0.07–0.16–0.37–
0.87–2.01–4.65–10.79–
25
ECMWF
reanalysis
Interactived
Grini et al. (2005)
Berglen et al. (2004);
Myhre et al. (2007)
11
LSCE
3.75◦ ×2.5◦ ×19 layers
1 mode
mmr=1.25 µm
σ 0 = 2.0
ECMWF
reanalysis
Interactived
Balkanski et al.
(2004)
Schulz (2007)
12
ECHAM5HAM
1.8◦ ×1.8◦ ×31 layers
2 modes
mmr=0.37,1.75 µm
σ 0 = 1.5,2.0
ECMWF
reanalysis
Interactive
Tegen et al. (2002)
Stier et al. (2005)
13
MIRAGE
2.5◦ ×2.0◦ ×24 layers
ECMWF
4 modes3
mmr=0.03,0.16,2.1,2.5 µm reanlysis
σ 0=1.6,1.8,1.8,2.0
Off-line
Ginoux et al. (2001)
Ghan and Easter
(2006)
14
TM5
6◦ ×4◦ global
1◦ ×1◦ North America
and Europe 25 layers
2 modes
mmr=0.22,0.59–
0.86 µm4
σ 0 = 1.59,2.0
Off-line
Dentener et al. (2006)
Krol et al. (2005); de
Meij et al. (2006)
ECMWF 12 h
forecast
1 For optical calculations the first bin is distributed into 4 bins (0.1–0.18–0.3–0.6–1.0) by assuming a mass fraction.
2 Emission follow lognormal with mmr 1.25 µm and σ 0 = 2.0.
3 The mmr values are global annual averages. They vary spatially and temporally with the mode volume and number mixing ratios.
4 The coarse mode diameter was varied for a fixed sigma in order to fit the data in Ginoux et al. (2001).
5 Unless otherwise specified, the winds correspond to the year 2000.
a National Aeronautics and Space Agency Data Assimilation Office.
b National Centers for Environmental Prediction.
c Goddard Earth Observing System version 3 Data Assimilation System.
d Some tunning was done in the emission flux, in general to fit a given dataset of observations.
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
than 1.2. In addition, in view of the coarse resolution of
the models (Table 1) and their difficulties to reproduce high
altitude sites, we exclude stations above 1000 m a.s.l. Additional comparisons at each AERONET site between each
model and AOD and AE are documented as time series in
http://nansen.ipsl.jussieu.fr/AEROCOM/.
AERONET dusty sites are grouped regionally into Africa
(AF), Middle East (ME) and Caribbean-American (C-AM)
sites. Stations not belonging to any of the defined groups
are considered separately. In each one of these groups stations are ordered from south to north. A list of the selected
dust sites based on the measurements for the year 2000 and
on the climatology constructed considering the multi-annual
database 1996–2006 is given in Table S3 in the Supplement.
2.4
AeroCom models
We use fifteen model outputs from the AeroCom aerosol
model intercomparison initiative (http://nansen.ipsl.jussieu.
fr/AEROCOM/). This initiative is a platform for detailed
evaluation of aerosol simulation by global models. It seeks
to advance the understanding of global aerosol and its impact
on climate by performing a systematic analysis and comparison of the results among global aerosol models including
a comparison with a large number of satellite and surface
observations (Textor et al., 2006). The comparisons conducted throughout the AeroCom project have revealed important differences among models in describing the aerosol
life cycle at all stages from emission to optical properties
(Kinne et al., 2006; Schulz et al., 2006; Textor et al., 2006,
2007; Koch et al., 2009; Prospero et al., 2010). The first of
the comparisons considered a total of sixteen global models.
Each model simulated the year 2000 using independentlyselected simulation conditions. This experiment “A” is documented in Textor et al. (2006) and Kinne et al. (2006). A
second experiment, “B”, was conducted in which the same
emissions were used in all models (Textor et al., 2007) and
where radiative forcing was assessed (Schulz et al., 2006). In
this present study we use the model outputs for the year 2000
of experiment A. For model TM5, which did not submit results for experiment A, we used results from experiment B
instead.
The model features that are important for this work are
presented in Table 1. For additional information on the models see Textor et al. (2006) and references therein. Four models from experiment A were excluded (ARQM, DLR, ULAQ,
UIO GCM) because their configuration was not meant to
simulate the dust cycle. Furthermore, some models that
joined the AeroCom project after the initial publication of
experiments A and B were included (CAM, Community Atmosphere Model). Model names have changed with respect to previous AeroCom publications; MPI-HAM is now
ECHAM5-HAM, KYU is now SPRINTARS and PNNL is
now MIRAGE. We use also the AeroCom median model
constructed at every grid point and for every month by comAtmos. Chem. Phys., 11, 7781–7816, 2011
Table 2. Models used to compute the AeroCom median for each
variable are indicated by an x. The variables are aerosol optical
depth at 550 nm (AOD), Angström exponent (AE), dust surface concentration (SCONC) and dust total deposition (DEPO).
Model
AOD
CAM
GISS
GOCART
SPRINTARS
MATCH
MOZGN
UMI
ECMWF
LOA
UIO CTM
LSCE
ECHAM5-HAM
MIRAGE
TM5
AE
SCONC
DEPO
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
x
puting the local median from the state-of-the-art AeroCom
A models. Since some variables are not available from all
models, the number of models used to construct the AeroCom median changes from variable to variable. Table 2 lists
the models used to compute each variable. In the following
comparisons and assessment the AeroCom median “model”
will be treated as any other model in this study. Its performance with respect to the other models will be discussed in
Sect. 4.
We also include in this study the aerosol model developed
within the Global and regional Earth-system Monitoring using Satellite and in-situ data (GEMS) project (Hollingsworth
et al., 2008). This model fully describes the atmospheric life
cycle of the main aerosol species; organic and black carbon, dust, sea salt and sulphate (Morcrette et al., 2009). It
is now fully integrated in the operational four-dimensional
data assimilation apparatus from the European Centre for
Medium Range Weather Forecast (ECMWF). Hereafter, we
refer to this model as ECMWF. Aerosol optical depth products from the Moderate resolution Imaging Spectroradiometer (MODIS) are assimilated to better estimate the aerosol
fields (Benedetti et al., 2009). In this study we only consider
simulations without data assimilation. For the evaluation of
the impact of data assimilation on the model performance see
Benedetti et al. (2009) and Mangold et al. (2011).
We evaluate the models in their performance to capture
the yearly mean and the seasonal variability. For the yearly
mean, we use scatter plots to analyse the model performance and we quantify this performance by computing the
root mean square errors (RMS), the mean bias, the ratio
of the modelled and observed standard deviation (sigma)
and the correlation (R). Considering the different range of
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
measurement of the variables used in the study and in order
to allow the intercomparison of the model performance for
the different variables, we include the normalized root mean
square (NRMS) error and mean normalized bias (MNB). We
use the NRMS to quantify the average model-observations
distance and the MNB for the average over- and underestimation. These statistics are computed as follows:
v
u S T
u 1 X X mij − oij 2
t
NRMS =
(1)
S i=1 j =1
oij
MNB =
S X
T
mij − oij
1X
S i=1 j =1 oij
(2)
where S is the number of stations considered and T the total
number of month used in the analysis for each station, oij
is the observed value at the station i and month j and mij
is the corresponding model monthly average at the closest
grid point to the station. For the seasonal analysis we use
Hovmoller-like diagrams where each row corresponds to a
given station. These diagrams are usually designed to indicate spatial propagation of features with time. However, we
choose to group the stations not in a geographically meaningful way as is usually done in Hovmoller diagrams but regionally to ease the assessment of the dust cycle. To evaluate the
model performance to reproduce the observed seasonal cycle
we use the MNB and the centred pattern root mean square
(CPRMS) error. The latter corresponds to the RMS error
when the bias has been removed (Taylor, 2001) and thus illustrates the average difference between the models and the
observations. We compute the CPRMS as the difference between the NRMS and MNB and obtain in fact a normalized
CPRMS (NCPRMS). The NRMS and MNB are computed as
follows:
v
u
N
u1X
Ml − O 2
t
100 ×
(3)
NRMS =
N l=1
O
N
Ml − O
1X
100 ×
MNB =
N i=1
O
(4)
where N is the number of models used in the study, O is the
array containing the elements oij defined above and Ml is the
equivalent array of each model l with the elements mij . Both
of these arrays have dimensions of S × T . We highlight that
in Eqs. (3) and (4) the sum is conducted over to the total number of models as opposed to Eqs. (1) and (2) where the sum
is conducted with respect to the stations and months and the
operation is repeated for each model. The observation array
O contains the data for each station and each month and remains therefore constant in Eqs. (3) and (4). To highlight this
fact we decide to omit the indexes on both arrays indicating
stations (i) and months (j ). This characteristic of O allows
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7789
us to continue computing CPRMS as the difference between
RMS and bias in spite of the normalization. The NCPRMS
is then calculated from
p
NCPRMS = NRMS2 − MNB2
(5)
In addition, we use the normalized standard deviation
(NSTD) to assess the spread among the models to simulate
the seasonal cycle or model diversity. The normalized standard deviation is computed as follows:
v
u
2
L
u 1 X
Ml − M̄
(6)
100 ×
NSTD = t
N − 1 l=1
M̄
where M̄ is an array of S ×T elements with the average over
all models for each station and month. Finally, we also include the Hovmollers of the individual models in the Supplement. Throughout the text we use the term “diversity”
as employed in Textor et al. (2006) namely “to describe the
scatter of model results”.
We computed the global model dust budgets for each one
of the models (Table 3). The annual emissions of the AeroCom models in Phase I are between 500 and 4400 Tg yr−1 .
This range exceeds the range of 1000–3000 Tg yr−1 usually
attributed to global models (e.g. Zender et al., 2004). The
global averaged dust AOD ranges from 0.01 to 0.053 with
80 % of the models having a value between 0.02 and 0.035.
The lifetime of dust aerosols is between 1.6 and 7.1 days for
most models.
Note that the model results used in the present analysis
correspond mostly to simulations submitted before the year
2005. Many of these models have been significantly improved since submitting their simulations. Therefore the results presented in this study do not necessarily represent the
current state of the models.
3
Results
The ability of each model to reproduce different aspects of
the desert dust cycle is evaluated by comparing them against
the data sets described above. We conduct the analysis on
a station by station basis. We use the AeroCom tools developed at the Laboratoire du Climat et de l’Environnement
(LSCE) to conduct the comparison and evaluation. The
global annual distribution of total deposition, surface concentration, AOD and AE of the AEROCOM median model
have been included in the Supplement (Fig. S1). The corresponding figures of the remaining models can be found
via the AeroCom web interfaces (http://nansen.ipsl.jussieu.
fr/AEROCOM/data.html).
3.1
Dust deposition
The comparison of total annual deposition and simulated deposition flux is presented in Fig. 1. See Table S1 in the Supplement for further information on the stations. The bias at
Atmos. Chem. Phys., 11, 7781–7816, 2011
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
Table 3. Mass balance for each one of the models. NaN represents variables not provided by model. MEE corresponds to the mass extinction
efficiency.
N
Model
Size
[µm]
Emission
[Tg yr−1 ]
Load
[Tg]
Deposition
[Tg yr−1 ]
Wet Depo
[Tg yr−1 ]
Dry Depo
[Tg yr−1 ]
Sedim
[Tg yr−1 ]
OD550
Dust
MEE
[m2 g−1 ]
Life Time
[days]
1
2
3
4
5
6
7
CAM
GISS
GOCART
SPRINTARS
MATCH
MOZGN
UMI
0.1–10
4313
1507
3157
3995
981
2371
1688
25.7
29.0
29.5
17.2
17.3
21.1
19.3
4359
1488
3178
3984
1070
2368
1691
1382
456
583
628
517
425
619
2300
352
120
2791
431
1943
1073
675
680
2475
565
122
NaN
NaN
0.035
0.034
0.035
0.024
0.033
0.022
0.021
0.69
0.60
0.60
0.72
0.96
0.52
0.56
4.6
7.1
3.4
1.6
5.9
3.3
4.2
8
9
ECMWF
LOA
0.03–20
(bins)
514
1276
6.8
13.7
750
1275
406
417
322
521
22
336
0.027
0.034
0.25
1.28
3.3
3.9
10
11
12
13
UIO CTM
LSCE
ECHAM5-HAM
MIRAGE
0.03–25 (bins)
1572
1158
664
2066
21.7
20.3
8.2
22.0
1571
1156
676
2048
681
616
374
1361
890
310
37
687
NaN
231
265
NaN
0.026
0.031
0.010
0.053
0.61
0.77
0.60
1.22
5.1
6.4
4.4
3.9
14
TM5
15
AEROCOM MEDIAN
1683
9.3
1682
295
592
794
0.013
0.68
2.0
1123
15.8
1257
357
396
314
0.023
0.72
4.6
(bins)
modes
–
most stations is within a factor 10 of the observations. All the
models in this study present a positive mean normalized bias
(MNB) in the deposition fluxes ranging from 0.1 to 140.3.
However, if the model CAM is not considered the maximum
MNB decreases to 13.4. In addition, if the measurements
from remote regions of the Southern Ocean and close to the
Antarctica (dark blue in Fig. 1), mostly overestimated by the
models, are excluded, seven from the 15 models produce a
negative MNB. While most models mainly overestimate the
deposition data from Mahowald et al. (2009) in the Antarctica, most of them underestimate the deposition in the Weddell Sea (13) in Antarctica (DIRTMAP; Tegen et al., 2002).
This difference in performance will be discussed in Sect. 4.
Most models (12 out of 15) underestimate the deposition in
the Pacific and the South Atlantic Ocean, while eight models
overestimate the deposition in Europe (green) and the North
Atlantic (orange) and nine in the Indian Ocean (dark green).
There is only one data set of deposition measurements in
the Taklimakan desert in central Asia (station H, purple in
Fig. 1). The model estimates of deposition at this site vary
over a large range, yet mainly underestimating the observations.
We expand the analysis conducted on 9 AeroCom models in Prospero et al. (2010) to estimate the wet and total
deposition of the FAMS network in Florida. Measurements
were conducted during almost three years and represent an
invaluable source of data to evaluate not only the simulated
wet and total deposition but also the simulated dust transport across the Atlantic. As in that study, to illustrate the
model performance we chose three representative stations
from the nine stations in the FAMS network. These stations
are oriented from south (Little Crawl Key) to north (Lake
Atmos. Chem. Phys., 11, 7781–7816, 2011
Barco) and therefore provide a latitudinal gradient of deposition in Florida. The general conclusions from that study
are also valid for the entire AeroCom model set of 15 models. Most models capture the seasonality of the deposition
and the dominance of wet deposition in the summer months,
from July to September, but only a few models capture the
magnitude of the deposition (wet and total) in this period most underestimate it (Fig. 3). The model performance deteriorates from south to north, reflecting model difficulties
in transporting the dust northward. In general, the models
overestimate the role of the wet deposition. They manage to
reproduce the fraction of wet deposition in regions where the
wet deposition dominates but fail to do so in sites dominated
by dry deposition (Table 4).
3.2
Surface concentration
We analyze the correspondence between observed and modelled yearly average surface concentrations at each site first
(Figs. 4 and 5) and then evaluate the simulated seasonality
(Fig. 6).
We first compare the simulated surface concentration to
short-term measurements from cruises (squares and filledin circles in Fig. 4) and long term measuring stations (diamonds in Fig. 4). Because major dust events occur on a
relatively small number of days per year (∼5 %, Mahowald
et al., 2009) and because of the limited number of ship
measurements, it is possible that the measurements miss
one (or more) of the events or that they actually coincided
with an event. The error in the measurements associated
with missing a dust event or coinciding with one is represented by the vertical lines in Fig. 4. For each model these
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7791
Table 4. Fraction of wet deposition [%]. The compilation is taken from Mahowald et al. (2010).
Obs
[%]
Bermuda
Amsterdam Island
Cape Ferrat
Enewetak Atoll
Samoa
New Zealand
Midway
Fanning
Greenland
Coastal Antartica
17–70
35–53
35
83
83
53
75–85
75–85
65–80
90
AeroCom
Median
CAM
ECMWF
GISS
GOCART
SPRINTARS
LOA
LSCE
MATCH
MOZGN
-HAM
ECHAM5
MIRAGE
TM5
UIO CTM
UMI
79
80
79
89
93
85
80
75
87
60
34
1
61
7
3
2
27
9
58
0
90
96
91
95
96
90
88
97
98
100
86
77
53
89
88
79
NaN
84
72
31
78
59
60
77
86
68
67
70
68
20
59
76
78
71
72
81
60
43
92
85
88
93
77
90
95
90
91
86
96
90
83
96
89
77
92
94
85
84
97
87
86
82
82
94
96
88
84
91
95
85
64
66
78
83
85
59
65
75
75
71
83
83
79
81
86
82
78
65
82
84
91
85
86
92
95
92
92
87
95
94
87
88
90
92
92
94
92
93
93
90
91
96
88
93
94
84
96
94
87
96
95
91
83
94
97
91
94
93
92
81
errors correspond respectively to 96 % and 20 % of the model
yearly average. In spite of the large uncertainties, these observations deliver valuable information in remote regions that
are seldom sampled (e.g. the Southern Ocean and South Atlantic Ocean) but where dust could have a great impact on
the biogeochemical cycle because of the high concentrations
of primary nutrients. All models mainly overestimate the
surface concentrations, exceeding in most of the cases two
orders of magnitudes with respect to the observed concentrations; the MNB varies between 34.08 and 1249.6. The
cases with large overestimation correspond mainly to shortterm cruise measurements in regions downwind of the main
dust sources. However, the models perform equally well
against cruise data in remote regions of the Southern Hemisphere (i.e. South Atlantic and Indian Ocean) as they do
against long-term measurements in other regions (diamonds
in Fig. 4); over and underestimation is mostly within two orders of magnitude. All models agree in mostly overestimating the cruise data in the Indian Ocean. In the South Atlantic
however, one third of the models underestimate the surface
concentration, one third overestimate it and finally one third
both under and overestimates the surface concentration.
We next compare the models to yearly averages of the
SEAREX and AEROCE data. The over and underestimation is mostly within a factor 10 (Fig. 5), except for Antarctica (stations 1, 8 and 9). The correspondence between modelled and measured surface concentration in most models improves in stations with higher values; the agreement is much
better in stations downwind of major dust sources (HIGH,
stations 17 to 22) than in the other two groups (Fig. 5). Likewise, the correspondence is better for stations of the second group (MEDIUM, stations 8 to 16) than for the first
one (LOW, stations 1 to 7). Half of the models present
larger differences with the observed surface concentrations
at sites associated with the Asian sources (stations 15, 20 and
22) than at stations measuring the trans-Atlantic dust transport from the Sahara (stations 18 and 19). The above suggests difficulties in simulating simultaneously the magnitude
of the dust emissions from Sahara and Asia (Tegen et al.,
2002). The remaining models produce similar performance
in reproducing surface concentrations associated with both
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deserts. All models underestimate the surface concentration
at Rukomechi in Zimbabwe (17), which measures the dust
emitted from the Kalahari Desert.
The yearly cycle of measured surface concentration and
a measure of the model performance to reproduce these observations (Sect. 2.4) are presented in Fig. 6. Each row corresponds to the monthly surface concentration of a network
station illustrated in Fig. 2. The measurements at each numbered station in Fig. 2 are presented in the numbered row in
Fig. 6. As in Figs. 2 and 5, we continue to group the stations as LOW, MEDIUM and HIGH according to their surface concentration regime.
In all three groups the underestimation is smaller than the
overestimation and in general no significant differences in the
MNB are observed between the groups. Likewise, no significant difference in the errors (CPRMS) is seen between the
three groups. The standard deviation reveals large spread in
the models to simulate the surface concentration, exceeding
in most of the cases 100 % and in some cases up to 500 %.
Yet important diversity exists between the models in the different group of stations. The largest diversity among the stations is seen in the Antarctica followed by the station on the
western Atlantic Ocean. This diversity will be discussed below in more detail.
The models on average underestimate the surface concentrations in the Antarctica stations (1, 8 and 9) throughout the
year in coherence with Fig. 5. In Mawson (1) and Palmer
(8) the largest errors coincide mostly with the period of low
surface concentration from March till September for the former and austral summer and early autumn for the latter. In
King George (9), on the contrary, large errors occur in both,
months with low and high surface concentration. The large
model diversity seen in these stations occur mainly from late
austral spring till early autumn in Mawson and throughout
most of the year in Palmer and King George. In Mawson,
periods of large diversity coincide mostly with month with
large errors.
The stations New Caledonia (2), Norfolk Island (12), Cape
Grim (10) and Jabirun (13) illustrate the Australian dust
cycle. While New Caledonia belongs to the LOW group,
characterized by surface concentrations below 1 µg m−3 , the
Atmos. Chem. Phys., 11, 7781–7816, 2011
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
Fig. 3. Modeled and observed wet (left) and total (right) dust deposition rates at three sites from the Florida Atmospheric Mercury Study
(FAMS) network: Lake Barco (LB), Tamiami Trail (TT), and Little Crawl Key (LCK). The black line is the mean of the 3 years of FAMS
data from 1994–1996. Vertical lines correspond to one standard deviation of the 3 yr average. Units are g m−2 month−1 .
stations of Cape Grim, Norfolk Island and Jabirun belong to
the MEDIUM group. It is interesting to compare the yearly
average at New Caledonia and Norfolk Island. These stations
are relatively close to one another (800 km) but they lie in
quite different dust regimes. Measurements suggest that Norfolk Island is impacted by Australian dust while New Caledonia lies outside of the northeast dust transport pathway from
Atmos. Chem. Phys., 11, 7781–7816, 2011
Australia (Mackie et al., 2008). Most models do not reproduce the different dust regimes in both stations and attribute
to New Caledonia the same range of measurement and seasonality as in Norfolk Island. This is illustrated by the overestimation throughout most of the year in New Caledonia and
large errors in Norfolk Island. In addition, important model
diversity is seen in these two stations mainly during austral
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Figure 4
N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
www.atmos-chem-phys.net/11/7781/2011/
Scatterplot of surface concentration from Mahowald et al. (2009) versus modeled one. Short-term measured Fe (and converted to dust by assuming a 3.5 % Fe in dust) during cruise are represented by filled-in circle. Data
corresponding to long term measurements are illustrated with diamonds while measurements of Aluminium or dust during cruise are indicated by squares. The colored dotted lines are estimates of the error in the model-data comparison
when the model represents the annual mean, while the data is taken on a few days. The methodology is discussed in the text (Sect. 2.2). Root mean square error (RMS), mean bias, ratio of modeled and observed standard deviation (sigma)
and correlation (R ) are indicated for each model in the lower right part of the scatterplot. Mean normalized bias and normalized root mean square error are given in parenthesis next to RMS and mean bias, respectively. The correlation
with respect to the logarithm of the model and of the observation is also given in parenthesis next to R . Black continuous line is the 1:1 line whereas the black dotted lines correspond to the 10:1 and 1:10 lines.
7793
Atmos. Chem. Phys., 11, 7781–7816, 2011
Fig. 4.
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
Fig. 5. Yearly averaged measured surface concentration from the network operated by the University of Miami versus modeled one at each
station, units are µg m−3 . Stations are grouped according to the regime of measured data into remote stations (orange), stations under the
influence of minor dust sources of the Southern Hemisphere or remote sites in the Northern Hemisphere (violet) and locations downwind of
African and Asian dust source (blue). The location of each station is illustrated in Fig. 2 and given in Table S2 in the Supplement. Root mean
square error (RMS), bias, ratio of modeled and observed standard deviation (sigma) and correlation (R) are indicated for each model in the
lower right part of the scatter plot. Mean normalized bias and normalized root mean square error are given in parenthesis next to RMS and
mean bias, respectively. The correlation with respect to the logarithm of the model and of the observation is also given in parenthesis next to
R. Black continuous line is the 1:1 line whereas the black dotted lines correspond to the 10:1 and 1:10 lines.
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Fig. 6. Monthly averages of measured surface concentration in µg m−3 are shown together with the mean normalized bias (MNB), the
normalized centred pattern root mean square error (CPRMS) and the normalized standard deviation (Sect. 2.4). In all subfigures, each row
corresponds to the seasonal cycle at one of the stations and the row for each station corresponds to the number presented in Fig. 2. The
stations have been grouped into Low (orange), Medium (violet) or High (blue) surface concentration sites (Sect. 2.2) and each group is
identified by a colored bar on the left side of the left hand figures. Stations are ordered from south to north within each group. White color
corresponds to months without measurements. For the individual figure of each model presenting the simulated values and their differences
(in %) with respect to observations see Figs. S2 and S3, respectively, in the Supplement.
summer. This may suggest difficulties by most models to
correctly simulate the transport of Australian dust to the east.
However, the differences between both stations could be related to the fact that the dust data are a climatology whereas
the model data are for a specific year. Dust emissions in Australia (Mackie et al., 2008) are highly episodic from year-toyear; consequently the model overestimation might actually
be the result of a small number of events that may have occurred in 2000 but not captured in the long-term measurements. The stations Cape Grim (10) in southern Australia,
Norfolk Island (12) offshore eastern Australia and Jabirun
(13) in northern Australia present all different seasonal cycles. In Cape Grim the months with maximum surface concentration are from late austral spring till early autumn while
in Norfolk Island the maximum is observed in September
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with an additional period of large concentrations from January till March and in Jabirun large concentrations are seen
from February till October with the maximum in July. The
MNB reveals that the models mainly underestimate the observations throughout most of the year at these stations and
the CPRMS shows that the largest errors do not necessarily coincide with months of maximum surface concentration.
Likewise, the largest model spread in these stations is seen
in periods of large surface concentration but not necessarily
coincident with the maxima. The large values of standard deviation correspond not only to a spread in the magnitude of
the simulated value but also on the duration and occurrence
of period of maximum concentration (Fig. S2 in the Supplement).
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The measurements in Hedo (20) and Cheju (22) present an
annual cycle with maxima in spring and minima in summer,
which corresponds to the maximum in dust storm activity
in China (Prospero et al., 1989; Prospero, 1996). An additional peak in surface concentration exists at these stations
in winter or late fall. The observations suggest that there is
substantial dust transport to these costal regions throughout
the year; however, some of this dust may be derived from
relatively localized sources. The station in Midway Island
(15), in central North Pacific and far off the east coast of
Asia, is also impacted by aerosol transport from Asia (Prospero et al., 2003; Su and Toon, 2011). The measurements
present a similar springtime maximum as the one in Cheju
and Hedo and low concentrations throughout the rest of the
year. The springtime maximum in Midway illustrates an important long-range dust transport of Asian dust. Most models
mainly underestimate throughout the year the surface concentration in Hedo and Cheju whereas they mostly overestimate it in Midway. In Hedo and Cheju the largest difference with respect to the observations occur from late boreal
autumn till observed early spring coinciding with the onset
of the period of maximum surface concentration. In Midway
however the largest errors occur from July to September after
the period of maximum concentration, yet important errors
are also seen in the month of May coinciding with the offset
of the period of maximum surface concentration. The model
spread remains mostly constant throughout the year in Midway while in Hedo and Cheju the largest diversity coincides
mostly with month with large errors.
The measurements in Barbados (18) and Miami (19) capture the transatlantic transport of Saharan dust. The former
presents an annual cycle with maximum between March and
October while the latter has maxima from July to August.
The surface concentration is mostly overestimated throughout the year and in particular at months with maximum surface concentration. However the largest errors with respect
to the observations are observed in boreal winter month, outside the period of maximum transatlantic Saharan dust transport. In general terms, the models reproduce the annual cycle of surface concentration in Barbados but present important diversity in both, the extension and intensity of the observed large surface concentration from March to October.
This diversity reaches its maximum in the winter months.
The model performance to simulate the surface concentration deteriorates towards the north in Miami, both in terms
of CPRMS and standard deviation. In general the models
present larger discrepancies with the observation in Miami
than in Barbados and model spread is also larger than in Barbados. All the above suggests that the models have more
difficulties to reproduce the annual cycle in Miami than Barbados. The data do not allow us to conclude whether this difficulty is due to problems in simulating the processes responsible for the northward extension of the transported transatlantic Saharan dust or to difficulties in simulating aerosol removal processes.
Atmos. Chem. Phys., 11, 7781–7816, 2011
To test the simulated seasonal cycle in dust transport
across the Atlantic and its northern latitudinal extend, we
compare the monthly mean model results to means of daily
measurements in Barbados (18) and Miami (19) for the year
2000 (Fig. 7). At both Barbados and Miami there is a clear
annual cycle in dust transport which yields a pronounced
summer maximum. The Barbados record differs from Miami in that the peak concentrations are higher and the dust
transport season extends through the late Spring and early
Fall. At Barbados the model results differ greatly from the
measurements over much of the year. The disparity is especially large in the summer. Over the reminder of the year,
principally October to May, most models underestimate the
surface concentrations. At Miami the model dispersion in
reproducing the measurements is smaller. However, some
models that reproduce the seasonal cycle at Barbados fail to
do so in Miami. This suggests that these models have problems in simulating the processes responsible for the northward displacement of the dust transport. The seasonal cycle for the year 2000 is not unusual and follows the average
from the 1996–2006 climatology (Fig. 7). However there are
some differences, most notably the peak in surface concentration in Miami in the year 2000 lags the climatology by
one month. At Barbados the climatology shows a maximum
in June with steadily decreasing values thereafter; however
in the year 2000 there are two maxima, one in June coincident with the climatology and one in August somewhat
above climatology whereas July is well below climatology.
Most models show a clear maximum in June, in agreement
with the seasonality of measurements and, like the dust climatology, they decrease steadily thereafter. It is notable that
a few models yielded very high monthly means at Barbados and Miami. Among the models with the highest values
are UIO CTM, CAM and GISS. While UIO CTM reaches
high monthly means at both stations (aprox. 450 µg m−3 in
Barbados and nearly 300 µg m−3 in Miami) CAM and GISS
largely overestimate the observations only in Barbados. Both
models simulate surface concentrations close to 100 µg m−3 .
3.3
Total aerosol optical depth
We now compare the models to AERONET total and coarse
mode AOD, first in terms of the average and then in their ability to reproduce the seasonal variability at dusty sites. The
average is constructed by using only selected months (as defined in Sect. 2.3) and therefore it is not a yearly average.
First we base the analysis on the climatology constructed using the multi-annual database 1996–2006 (Sect. 2.3) and then
on the data of the year 2000. In both cases, dusty stations
have been grouped regionally into African (AF), Middle East
(ME) and Caribbean-American (C-AM) stations and stations
elsewhere (Fig. 8). In each of these regions the stations are
organized from south to north.
A total of 25 AERONET stations are considered as dusty
sites based on the AE and the AOD when climatological data
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Fig. 7. Measured and simulated surface concentration in Barbados and Miami. Measurements of the year 2000 are presented by the black
continuous line and the climatology (Fig. 6) is presented by the black dashed line. Units are µg m−3 .
23
22
21
19
20 18
17
10
7
6
24
8 9
4
1
5
25
15 16
14
11
13 12
3 2
Fig. 8. Location of selected AERONET dusty sites based on
the climatology built from the multi-annual database 1996–2006.
Dusty stations are grouped regionally; Africa (orange), CaribbeanAmerica (blue), Middle East (violet) and elsewhere in the world
(black). Names and locations for each selected station are given in
Table S3 in the Supplement.
are used (Sect. 2.3, Fig. 8). Names and locations for each
one of these sites are given in Table S3 of the Supplement. In
general the modeled AOD is within a two-fold range of the
observations at most sites (Fig. 9). The mean normalized bias
(MNB) of all models varies between −0.44 and 0.27 while
the normalized root mean square error (NRMS) varies between 0.3 and 0.6. More than half of the models (8 out of 15)
produce a negative MNB varying between −0.44 and −0.03
and NRMS varying between 0.3 and 0.6. For models mainly
overestimating the AOD, the MNB varies between 0.02 and
0.27 and the NRMS between 0.3 and 0.5. The data show in
general higher AOD at African stations than at those in the
Middle East, which in turn have larger values than the Amerwww.atmos-chem-phys.net/11/7781/2011/
ican stations. In general, the models reproduce this gradient
between regions. Eight of the 15 models underestimate the
averaged AOD at all or almost all American stations. Some
models do not reproduce the observed gradient in AOD between African and Middle East dusty stations, instead producing similar AOD in the Middle East and in Africa. Others
overestimate the AOD for the African stations. Considering
the closeness of the stations to the sources in both regions, the
overestimation of AOD points to an overestimation of dust
emissions or underestimation of the removal in the Middle
East and/or Africa. Another cause could be the use of wrong
size distribution with the consequent impact on the estimation of the extinction. This aspect will be further developed
in Sect. 4. Finally, twelve models underestimate the AOD
in Kanpur (25) in northern India, again suggesting that most
models underestimate emissions of the Great Indian Desert
or overestimate the removal.
The seasonality of the AOD climatology in Africa
(Fig. 10) is characterized by high AOD with maximum values from December to April in the most southern stations
shifting progressively to July through September in the most
northern African stations. In general the underestimation coincides with the months of maximum AOD. Additional underestimation is observed from July till October in most stations. The overestimation of AOD in general corresponds to
the month of late fall and early winter (November and December) and the month preceding the month of maximum
AOD and presents thus also a progressive shift from late
winter till late spring in stations from south to north. Exceptions to the above described behavior are the southern
most stations of Ilorin (station 1) and Djougou (2) in Nigeria
and Benin respectively where the underestimations extends
throughout the year and in western Sahara at Dahkla (10)
where the AOD is overestimated throughout most of the year.
The seasonal cycle in Ilorin and Djougou is reproduced by
most models and the underestimation might be indicative of
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Fig. 9. Averaged AOD at 550 nm versus modeled one at dusty stations of the AERONET network. Data from the climatology based on
the multi-annual database 1996–2006 are used. Stations are regionally grouped into African (orange), Middle East (Violet) and CaribbeanAmerican stations (Blue) and stations elsewhere (black). Location of each station is illustrated in Fig. 8. Name and location of each station
is given in Table S3 in the Supplement. Root mean square error (RMS), bias, ratio of modeled and observed standard deviation (sigma)
and correlation (R) are indicated for each model in the lower right part of the scatter plot. Mean normalized bias and normalized root mean
square error are given in parenthesis next to RMS and mean bias, respectively. Black continuous line is the 1:1 line whereas the black dotted
lines correspond to the 2:1 and 1:2 lines.
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Fig. 10. AERONET AOD at 550 nm is shown together with the mean normalized bias (MNB), the normalized centred pattern root mean
square error (CPRMS) and the normalized standard deviation (Sect. 2.4). In all sub-figures, each row corresponds to the seasonal cycle at
one AERONET station. They have been grouped into African (AF, orange), Middle East (ME, violet) and Caribbean-American (C-AM,
blue) stations and stations elsewhere in the world (OT, black). Each one of these groups is identified by a coloured bar on the left side of the
left hand figure. Stations are ordered from south to north within each group. The row for each station corresponds to the number presented in
Fig. 8. Name and location of each station is given in Table S3 of the Supplement. White color corresponds to month without measurements
or month not complying with the selection criteria (Sect. 2.3). AERONET data correspond to the climatology based on the multi-annual
database 1996–2006. For the individual figure of each model presenting the simulated values and their differences (in %) with respect to
observations see Figs. S4 and S5, respectively, in the Supplement.
difficulties in simulating the emissions or removal processes.
In Dahkla on the contrary the overestimation is the result of a
very long period with large AOD simulated by most models.
The largest differences with respect to the observations (illustrated by the CPRMS) coincide in general with the months
where the AOD is overestimated. The largest errors are seen
in Djougou in the first half of the year and December. The
spread between the models varies mostly between 30 and
45 % with some isolated month where the spread varies between 50 and 60 %. The model diversity presents in general
a seasonal cycle with minimum in summer and early autumn
and maximum the rest of the time. Contrary to the cycle asso-
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ciated to the MNB and CPRMS, maximum diversity or standard deviation is seen in months with both, large and small
AOD.
In the Middle East there is a seasonal cycle with maximum
AOD from May–June to September (Fig. 10). In general
the simulated AOD is mostly overestimated from January to
August and underestimated afterwards. This period of overestimations in general corresponds to the months of maximum AOD and those preceding it. Again, the largest errors
are mostly seen in month where the AOD is overestimated.
Models present larger diversity in simulating the AOD in the
Middle East than in Africa and the spread between models is
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mostly coincident with periods of overestimation and large
errors described above. Exceptions to this are the month of
November and December where large values in standard deviation are seen in periods of small error and underestimation
of the AOD.
At Caribbean-American (C-AM) stations there are large
periods that have no data, mostly in the early and late months
of the year (Fig. 10). The magnitude of the model diversity is in general larger than at African stations. The AOD is
mostly underestimated throughout the year except for the boreal winter months in La Parguera (20) in Puerto Rico. This
station presents also the largest errors (CPRMS) mostly in
months with low AOD. In general large errors are observed
at stations affected by transatlantic dust transport (stations
18 to 21). In addition, at these stations, the largest spread between the models is coincident to the months with largest
errors. With respect to the individual stations, no model
simulates the AOD in Paddockwood (station 23) in central
Canada (Fig. S4 in the Supplement). At stations affected by
the transatlantic dust transport (stations 18 to 21) most models capture the higher AOD in the summer month of June to
September. At Surinam (17), in northern South America, a
single summer month presents an overestimation, large discrepancy with the observations and large model diversity. At
Capo Verde (station 24), offshore western Africa, most models (10) simulated the higher AOD from June to September;
however they mainly overestimate the AOD throughout the
remainder of the year. In Kanpur (station 25), northern India, on the contrary, models capture the seasonality but the
magnitude is mostly underestimated (by 12 of the 15 models).
In the analysis of data for the year 2000 fewer stations
are included because the number of available stations for this
particular year is smaller. Only 8 AERONET stations from
a total of 446 met the requirements of a “dusty” station described in Sect. 2.3 (Table S3 in the Supplement, Fig. 8).
Note that we use the same numbers to identify the stations as
used in Figs. 9 and 10.
The averaged AOD is again reasonably well simulated by
almost all models (Fig. S6 in the Supplement). The simulated
AOD is within a factor two of the observed AOD at almost
all stations and for almost all models. The MNB varies between −0.38 and 0.4 and the NRMS between 0.1 and 0.5 for
all models. The same 8 models that underestimate the climatology also underestimate the data of the year 2000 with
MNB between −0.38 and −0.04. While the NRMS presents
larger variability between models for data of the year 2000
compared to the climatology, the models produce in general
smaller errors in simulating the data of the year 2000. In addition, except for two models, all models produce a larger
correlation (R) when simulating the AOD at all stations for
the year 2000. An AOD grouping similar to the climatology
is observed among the dust regions; African stations yield
the largest AOD followed by Middle East and then America.
About half of the models (7) reproduce the AOD grouping
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observed in the three defined regions. Eight models underestimate the AOD at American sites while six of the 15 models
overestimate the AOD in all African stations. A few models
(4) systematically underestimate the AOD at all or almost all
of the dusty stations.
Contrary to what was seen for the climatology where the
underestimation coincided mostly with months of maximum
AOD, for the year 2000 the AOD is mainly overestimated
at all stations and throughout most of the year (Fig. S7 in
the Supplement). Exceptions to this are Ouagadougou (4) in
Burkina Faso and Surinam (17) in northern South America.
Yet the large errors (CPRMS) are observed, as for the climatology, at months where the AOD is overestimated. The
maximum CPRMS in fact coincide with the maximum MNB.
In addition the largest diversity corresponds to month with
overestimation and large errors.
In general most models reproduce the shifting of maximum AOD in African stations from March in Ouagadougou
to June in Dakar (8) western Sahara, yet no model reproduces the second maximum in October in Ouagadougou and
Banizoumbou (6) in Niger. They either fail to reproduce the
second maximum at all, simulate it delayed by one month, or
it is too long in duration (see Fig. S8 in the Supplement). All
models simulate year-round dust transport off Africa at Capo
Verde (24) offshore western Africa mostly overestimating it.
While a large number of models simulate the two maxima
present in the observations, a few models (4) produce only a
single maximum. This last finding may indicate deficiencies
in reproducing the mechanism responsible for transporting
dust offshore. At the Caribbean-American stations in Barbados and Puerto Rico, all models reproduce the observed
transatlantic dust transport as illustrated by the AOD in June
and July. Observations suggest that only dust emissions responsible for the maximum in Dakar are transported across
the Atlantic. None of the models reproduce the seasonal cycle observed in Surinam in northern South America which
shows a maximum AOD in winter months. This winter peak
is linked to the seasonal southward displacement of transAtlantic African dust plume during winter as seen in various
satellite products (e.g. Husar et al., 1997) and characterized
by measurements along the coast of French Guiana (Prospero
et al., 1981) and over the Amazon (Swap et al., 1992). There
is no relationship between the ability of models to reproduce
the yearly cycle of AOD over Africa and Caribbean-America
and the ability to reproduce the cycle in the Middle East.
3.4
Coarse mode aerosol optical depth
The coarse mode AOD corresponds to the aerosol optical depth of particles with radius larger than 1 µm, i.e. sea
salt and desert dust. Its retrieval depends on concurrent
multiple-angle sky observations (almucantar and azimuth
plane measurements). Because these measurements are often precluded by sky conditions, less coarse mode AOD
is retrieved than total AOD which requires only direct sun
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Fig. 11. Same as Fig. 10 but for coarse mode AOD. Same stations as the ones used for total AOD and illustrated in Fig. 8 are considered. Stations Bandoukoui (3) and Bidi Bahn (7) do not have coarse mode AOD for the selected period. For the individual figure of each
model presenting the simulated values and their differences (in %) with respect to observations see Figs. S10 and S11, respectively, in the
Supplement.
measurements. As a consequence of this difference in number of available measurements, the monthly mean coarse
mode AOD can show larger values than the monthly mean
total AOD.
The coarse mode AOD climatology (Fig. 11) has a seasonal cycle similar to the total AOD (Fig. 10). Note that
stations Bandoukoui (3) and Bidi Bahn (7), both in Burkina Faso, do not have coarse mode AOD measurements and
fewer qualifying data for the C-AM stations are available.
The coarse mode AOD represents more than half of the total AOD in periods of maximum total AOD, illustrating the
dominance of coarse dust particles. The models in general
reproduce this dominance of coarse dust particles and produce seasonality similar to the total AOD. However the differences with respect to the observations in terms of Bias,
CPRMS and standard deviation are increased compared to
the total AOD. The overestimation is in general larger for the
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coarse mode AOD than the total AOD except for the African
stations 1 to 6. In addition to a general increase in the error
to reproduce the coarse mode AOD with respect to the total AOD, the large errors are not necessarily associated to an
overestimation as was seen with the total AOD. Yet the maximum in CPRMS are still linked to months were the coarse
mode AOD is overestimated. Finally, larger model diversity
exists for all stations and throughout the year.
The observed coarse mode AOD for the year 2000 (not
shown) presents the same features as the climatology in the
few qualifying month available. There is a similar seasonality in coarse-AOD as total AOD and a dominance of coarse
mode dust particles in months of maximum total AOD. Most
models reproduce this seasonality and simulate a dominance
of coarse mode particles in periods of maximum AOD. Furthermore, the models present in general larger errors and
larger diversity for the coarse mode AOD than the total AOD.
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Month overestimating the coarse mode AOD do not necessarily coincide with months where the total AOD is overestimated (not shown).
3.5
Angström Exponent
We now analyse the climatology of the Angstrom Exponent
(AE) for dusty sites. Again, we start by analyzing the averaged AE (Fig. 12) and then the seasonal cycle at the 25
stations selected with climatological data (Fig. 13). Next we
reproduce this analysis with the 8 stations selected using the
data of the year 2000 (Figs. S14 and S15 in the Supplement).
In general the over/under estimation of the models is
within a factor of two of the observations (Fig. 12). Yet the
errors (NRMS) and bias are larger than for the AOD suggesting that models simulate better the total AOD than the AE
and thus reproduce better the aerosol load than the size distribution. The sole exception to this is MATCH that shows
larger NRMS for the AOD than the AE. Only four models
mainly underestimate the AE, indicating that these models
simulate larger particles than is observed. With the exception of MIRAGE, models overestimating the AE produce a
smaller bias (MNB from 0.13 to 0.67) than the ones underestimating the AE (MNB from 0.25 to 0.75). However, the
opposite is seen for the NRMS; the models underestimating
the AE (0.4–0.8) have smaller errors than those overestimating the AE (0.5–0.9). Nine of the 13 models underestimate
AE in the Middle East because they simulate larger particles than observed. Nearly all models overestimate the AE
in a good number of Caribbean-American stations. Greater
diversity is found for simulations of the AE at African stations. Except for stations Ilorin (1) and Djougou (2) in Nigeria and Benin respectively, the measurements in the Middle
East show larger AE average than in Africa, thus indicating
the predominance of smaller particles in the former. This
larger AE could be due to the influence of anthropogenic
aerosols and not necessarily dust aerosols only. The AE at
the Caribbean-American stations spans the range of values
observed in Africa and the Middle East. Recall that only
months dominated by coarse dust aerosols or with mixtures
of coarse and fine aerosols are analyzed, and that therefore
observations-model discrepancies could also be due to anthropogenic aerosols. Only half of the models reproduce this
difference in AE between the Middle East and Africa, while
ten models simulate the wide range of AE in American stations.
The models mostly overestimate the AE throughout the
year or during most of it at stations in Africa, CaribbeanAmerica and elsewhere (Fig. 13). A few models (3) fail to
reproduce the AE variability at all stations and produce rather
homogenous yearly cycle (Fig. S12 in the Supplement). Only
in the Middle East the models also underestimate the AE, this
mainly during late fall and winter when mixture of large and
fine particles dominate but also partly from March till July
when large particles dominate.
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Except for the two most southerly stations, the AE in
Africa shows that coarse aerosols (AE < 0.4) dominate in
months with maximum AOD; the coarse mode dominates in
spring in southerly stations and shifts progressively to summer and early fall in the northerly stations. This feature is
captured by a large number of models (8 out of 13), with
most models underestimating the duration of period with
small AE. In stations 3 to 9 the coarse aerosol dominance
extends beyond the period of maximum AOD. The largest
models errors to reproduce the AE are seen in month where
the coarse model dominates. The simultaneous overestimation of AE and large model errors in reproducing the AE in
periods where the coarse mode dominates, suggest that the
models in general simulate too much or too small fine particles. This issue will be addressed in more detail in Sect. 4.
The standard deviation reveals that the largest model diversity exists mainly from February till June in stations 2 to 9
mostly coincident with months of coarse mode dominance.
Station 1 and 10 show the smallest and largest spread respectively extending throughout the year.
In the Middle East only a few models (6) manage to reproduce the dominance of large particles observed in the month
preceding the period of high AOD and the mixture of fine and
coarse particles observed during the month of high AOD. In
general models overestimate the AE before and during the
onset of the period of high AOD and underestimate it afterwards. Except for the stations in Solar Village and Barahin,
two periods with large diversity are observed, one in July
and August coincident with the months with maximum AOD
and another one in March and April coincident with months
dominated by coarse mode AE. Solar Village and Barahin
present large diversity throughout most of the year. The error with respect to the observations coincides in general with
the period of large diversity except for the months of March
and April.
Most models simulate the yearly cycle at the American
stations 18 to 21 consistent with a dust contribution of large
African dust aerosols in the summer months. In contrast
models have difficulty in reproducing the relatively small AE
observed in Surinam (17) from February to May, as revealed
by large errors as well as large overestimation of the AE.
However, the models present small model diversity during
these months. This large errors and bias suggests difficulties
to reproduce the Winter-Spring transport of African dust to
South America as described above.
The station at Capo Verde (24) is dominated by large particles throughout the year, illustrating the occurrence of dust
transport off the coast of western Africa throughout the year.
Models differ from observations mainly in the onset and duration of periods characterized by large particles. Finally
most models have difficulties simulating the yearly AE cycle with the dominance of large particles from May to July
in the station at Kanpur in Northern India (25).
As for the climatology, for most models the errors
(NRMS) and bias in AE are larger than for the AOD.
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Fig. 12. Same as Fig. 9 but for Angström exponent.
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Fig. 13. Same as Fig. 10 but for Angström exponent. For the individual figure of each model presenting the simulated values and their
differences (in %) with respect to observations see Figs. S12 and S13, respectively, in the Supplement.
Exceptions are the models MATCH and UIO CTM where
the AE error is smaller and ECMWF, LSCE, TM5 and
UIO CTM where the AE bias is smaller. Furthermore models overestimating the AE (excluding MIRAGE) produce in
general smaller MNB than those underestimating it. The
same four models yielding a negative bias with the climatology also produce one with 2000 data (Fig. S14 in the Supplement). However contrary to what is seen with the climatology, the models overestimating the AE (excluding MIRAGE)
have a smaller NRMS (between 0.2–0.7) than those underestimating it (between 0.3–0.8). The averaged AE for the year
2000 shows that the smallest particles (largest AE) are observed in Solar Village (station 15) in the Middle East and
Surinam (17) in northern South America while African stations present values smaller than in the Middle East but larger
than the two stations in the Caribbean (Roosevelt Roads, PR
and Barbados, WI). This larger AE in Africa than in the
Caribbean suggests a greater ratio of large to small particles
across the Atlantic than in the source regions. Possible expla-
Atmos. Chem. Phys., 11, 7781–7816, 2011
nations for the larger particles across the Atlantic are the influence of pollution from Europe and biomass burning from
the low latitudes and/or the aging of air mass as they cross
the Atlantic. In this long range transport small particles are
lost due to chemical reactions (growing larger) and to agglomeration during cloud processing. However, the smaller
AE average across the Atlantic can also be a numerical artifact due to fewer selected month used in the computation
of the average in the Caribbean. While in African stations
the average is the result of considering several months that
combine large and small AE, in the Caribbean stations fewer
months are considered and they are dominated by small AE.
In fact the station of Surinam (17) in northern South America with a larger record presents an AE average larger than
in African stations. At Capo Verde (24), offshore western
Africa, the observed averaged AE is comparable to values
observed in Barbados (18) and Roosevelt Roads (21). Eleven
of the 13 models reproduce the observed AE for the year
2000 with absolute differences falling within a factor two
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of the observations. While most models (10 out of 13) underestimate the AE in the Middle East they produce larger
diversity when simulating the AE in Africa and CaribbeanAmerica. However, many models (9) reproduce the AE in
Barbados and Roosevelt Roads better than in African Stations.
The annual cycle of AE at dusty stations during the year
2000 has features similar to those seen in the climatology.
Contrary to the climatology, for the year 2000 the models
mainly overestimate the AE in all regions and throughout
most of the year, in particular in periods when the coarse
mode dominates (Fig. S15 in the Supplement). In general
the models simulate better the year 2000 than the climatology as illustrated by smaller biases and errors. While the
model diversity is larger in the C-AM stations for the year
2000 than for the climatology the opposite is true for Solar
Village. In African stations the model spread is larger for
the year 2000 in Ouagadougou (4) in Burkina Faso while in
Banizoumbou (6) and Dakar (8) in general no large differences are observed. As seen with the climatology, a large
number of models (7) reproduce the AE seasonality in Barbados (6) and Roosevelt Roads (7) but almost all models fail
to reproduce the presence of large particles from February
to April in Surinam (5). This yearly cycle is consistent with
the southward displacement of the dust transport in winter
months described in Ginoux et al. (2001) and as measured in
French Guiana (Prospero et al., 1981) and over the Amazon
(Swap et al., 1992).
4
4.1
Discussion
Surface variables
Most models simulate the dust deposition measurements
within a factor 10 of the observations. Even though all the
models produce a positive MNB for the total deposition,
models yield both over and under-estimations that vary with
the location of the data. While many models overestimate
deposition in the Indian Ocean (9 out of 15) and Europe and
North Atlantic (8 out of 15), most models underestimate the
deposition at remote regions of the Pacific and the South Atlantic Ocean (12 out of 15). Only a few data of total deposition exist in HNLC regions to assess the model performance
to reproduce deposition in regions sensible to iron contributions. In addition, the predominant model performance to reproduce deposition in these regions varies depending on the
location and dataset considered. While the fluxes near the
Antarctica are mostly overestimated, the one in the Southern Ocean is mostly underestimated (station 13 in Fig. 1).
Different dust regimes influence each of these sites as indicated by the magnitude of the measured deposition. Difficulties in simulating these dust regimes and the dust transport
to remote regions might explain this varying model performances. However, data quality cannot be discarded as source
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of the difference. Mahowald et al. (2009) points to the errors
that can result from estimating the dust fluxes from sediment
traps. On the other hand, the Antarctic dust deposition fluxes
used in Mahowald et al. (2009) result from measurements
of dissolved iron in snow that are known to be too low (Edwards and Sedwick, 2001). In order to reduce the uncertainty
associated to the model performance to reproduce the atmospheric iron contributions in HNLC regions, further measurements and model studies are needed. The overestimation in
the Northern Hemisphere may suggest a problem in representing the intensity of emissions, the size distribution of the
transported dust, the transport itself and/or the representation
of deposition flux. At present because of data limitations it
is not possible to link the differences between models and
observations to any specific process. When comparing the
models against long-term measurements of total and wet deposition taken in Florida (Prospero et al., 2010), models capture the seasonality of the deposition and the dominance of
wet deposition but most underestimate the magnitude. Furthermore, the performance deteriorates from south to north.
These differences could be due to difficulties in simulating
the northward transport of dust or the removal processes.
Observations suggest that wet deposition dominates over
dry deposition over most ocean and remote regions of the
world (Mahowald et al., 2011). Models are able to capture
this dominance of wet deposition, but tend to overestimate it
at many locations, especially in those where it is not the dominant removal process (Table 4). We agree with Wagener et
al. (2008), Mahowald et al. (2009) and Prospero et al. (2010)
that more measurements of deposition fluxes are needed, in
particular in the HNLC regions of the Southern Hemisphere,
to better estimate the atmospheric iron contribution into the
oceans. Ideally such measurements should extend for a year
or more considering that the large fraction of the annual deposition occurs in episodic events of just a few days (Prospero et al., 2010; Mahowald et al., 2009). In addition, these
measurements should also split between wet and total deposition, as done in Prospero et al. (2010), considering the uncertainty of the contribution of wet deposition in total deposition over ocean (Jickells et al., 2005). However it should be
noted that there is a severe problem in measuring dry deposition. The use of buckets or surrogate surfaces as collectors
does not reflect real world conditions; the aerodynamics of
these collectors and their surface properties are very different
from natural surfaces such as bare soil, grasses or the ocean
surface (Prospero et al., 2010). As a result dry deposition is
typically calculated based on particle size distributions; such
estimates are prone to large uncertainties which are typically
quoted as plus/minus a factor of three (Duce et al., 1991) but
which could well be larger. In the meantime, before such
long-term measurements are available alternative techniques
to evaluate deposition may be necessary. One such method
is to simulate the deposition and advection of dissolved aluminium in the surface ocean and to compare against surface
ocean aluminum measurements (Han et al., 2008). These
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could also be inverted to estimate deposition. But this technique is complicated by uncertainties in the solubility of dust
aluminium and the properties of the dust itself.
The model performance in simulating surface concentration depends on the data sets used. For example when using
measurements from cruises, all models agree in mainly overestimating the surface concentration by mostly a factor of ten
up to a hundred whereas the underestimation is mostly limited to a factor ten. The cases with large overestimation correspond mainly to short-term cruise measurements in regions
downwind of the main dust sources. However, for the cruise
measurements in remote regions of the Southern Hemisphere
the models perform equally well as they do against long-term
measurements in other regions. When using long-term measurements of the SEAREX and AEROCE network, on the
other hand, the overestimation is within a factor of ten with
respect to the observations. It has to be noted however that
the cruise measurements correspond to short-term measurements and if the sampling error due to missing dust events is
taken into account the large overestimation is reduced (up to
96 %) and the performance resembles the one observed with
long-term measurements. In spite of the large uncertainties,
these observations deliver valuable information in remote regions that are seldom sampled (e.g. the southern Ocean and
South Atlantic ocean). While all models agree in overestimating the cruise data in the Indian Ocean, large model diversity exist in simulating the surface concentration in the
South Atlantic varying from some models overestimating the
observations, other underestimating it and some of the models both over and under estimating the surface concentration.
Much of this region is characterized as HNLC; consequently
dust deposition can have a great impact in the biogeochemical cycle.
Recall that for both surface concentration and deposition
the period when the data were taken is not coincident with
the simulated year, a factor which could explain part of the
model-observation differences since most models constrain
the dust cycle with reanalyzed winds of the year 2000 (Table 1). However, the large over/under estimation by most
models points to other issues. Because of the episodic nature
of dust events and the few days in which they occur (Prospero
et al., 2010; Mahowald et al., 2009), short-duration measurements risk missing dust events and should therefore be applied with care for model evaluation.
Particle size is also an important factor and a source of discrepancies when comparing deposition and/or surface concentration to model outputs. The representation of size distribution of mineral dust is a fundamental parameter to simulate and understand its impact; while the fine mode controls
the direct impact on radiation and cloud processes, the coarse
mode governs deposition and hence its biogeochemical impact (Formenti et al., 2010). Variables integrated over all
size classes, as available for this study, prevented us from exploring the impact of the different representation of the size
distribution in each model on its performance in simulating
Atmos. Chem. Phys., 11, 7781–7816, 2011
the different observations. Therefore, knowledge of the size
distribution of both measurements and model would allow a
more in-depth model evaluation and assessment of its performance. We therefore suggest that size-resolved surface
concentration and deposition be archived in future model experiments.
4.2
Vertically integrated variables
The models reproduce the retrieved AOD and AE within a
factor of two. Furthermore, most models present a better
performance in simulating the total aerosol load than the size
distribution of dust particles as revealed by smaller errors and
bias associated to the averaged AOD. In general in Africa and
Caribbean-America the models underestimate the AOD climatology in months of maximum AOD and overestimate the
AE throughout most of the year. While the models present
the largest errors in AOD mainly in months with low values
the largest error in reproducing the AE occur in months of
maximum AOD dominated by coarse particles. In contrast
to stations in Africa and Caribbean-America, in the Middle
East models not only overestimate the AOD during month
with maximum AOD but also in the month preceding it. The
AE is overestimated before and during (May to July) the onset of the period of high AOD and underestimated the rest
of the year. In general the models present larger diversity in
simulating the AOD in the Middle East than in Africa. When
compared to the year 2000, both AOD and AE are mostly
overestimated in all considered dust regions.
Models capture the transport of dust across the coast of
West Africa to the Atlantic throughout the year as illustrated
by comparisons with measurements at Capo Verde, located
600 km to the west of the African coast. The models also
reproduce the trans-Atlantic dust transport as characterized
by measurements at Capo Verde, and Barbados, 4000 km to
the west. While all models reproduce the AOD seasonality
in Barbados, only 7 reproduce the seasonality of AE in this
station.
The trans-Atlantic dust plume undergoes a seasonal displacement that is linked to movements of the Intertropical
Convergence Zone (ITCZ). During the boreal summer the
ITCZ reaches its most northern position, and winds carry
dust to the Caribbean. During the winter the ITCZ reaches
its southernmost position, and dust is carried to South America (Prospero et al., 1981; Swap et al., 1992; Ginoux et al.,
2001). This seasonal transport cycle is reflected in the AOD
record in Surinam (northern South America) which has a
minimum in the summer at the time when the AOD at Barbados reaches the annual maximum. Most models successfully
simulate the AOD seasonal cycle in Barbados but they do not
reproduce the minimum AOD confined to the summer month
in Surinam. This might indicate problems in simulating the
general circulation in the tropics and/or removal process coincident with this southward shift of the transatlantic dust
cloud.
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Recall that the AOD and AE analysis is based on months
dominated by coarse aerosols or the mixture of fine and
coarse aerosols. Therefore the discrepancies between observations and model can also be explained by the influence of anthropogenic aerosols. However, since in African,
Caribbean-American and Other stations the months of maximum AOD are also characterized by coarse particles we
are confident that the atmospheric aerosols, at least in these
months, are dominated by desert dust and therefore the
model performance is associated to the models ability to simulate the dust cycle. In the Middle East, in contrast, the period of maximum AOD is influenced by both large particles
and mixtures of fine and coarse particles and these fine particles are most likely due to the presence of anthropogenic
aerosols. Eck et al. (2008), in studies in a network of 14
AERONET photometers in the United Arab Emirates, observed increases in AE coincident with the presence of increased concentrations of fine particles which they attributed
to sources in the petroleum industry.
4.3
Emissions
There are no datasets of measured dust emissions that could
be used in this study. Still, evaluation of the simulated combination of AOD and AE allows us to make inferences about
the simulated emissions. Since the scattering efficiency
varies according to the size, the AOD is not only dependent on the aerosol burden but also on the size distribution;
smaller dust aerosol particles scatter light more efficiently
than larger ones, i.e. for the same burden air masses containing higher concentrations of smaller particles will yield
larger AOD. Based on the latter factor, the combination of
AE and AOD measurements can be used to infer whether
the emissions are over- or under-estimated. To illustrate this,
let’s suppose that a model simultaneously overestimates the
AOD and underestimates the AE close to the source. In order to increase the AE and thus reduce the underestimation,
a larger fraction of fine particles is necessary. This can be
achieved by either augmenting the emissions of fine mode
particles, which would increase even more the AOD, or by
reducing the emissions of coarse particles, leading to a reduction of the AOD. Therefore, a simultaneous overestimation of the AOD and underestimation of the AE points to an
overestimation of the mass emissions especially of the coarse
dust particles if interference from other aerosol components
can be excluded. Likewise, the simultaneous underestimation of the AOD and overestimation of the AE, points to an
underestimation of the coarse dust emissions. In both cases,
however, fine mode dust emission adjustments might additionally be needed. Simultaneous over- or underestimation
of both AOD and of AE precludes inferring whether the intensity of the source has been over- or under-estimated. We
need to improve the simulation of the dust size distribution
in models before we can attempt to quantify adjustments to
emissions.
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We present in Fig. 14 the results of applying the above
considerations to the comparison with the AERONET data.
It should be noted that for the judgement on the over- and
under-estimation of the emissions based on the AOD and AE
other simulated processes might be responsible such as sedimentation, wet deposition, dry deposition, horizontal and
vertical transport. These processes have a lesser impact on
stations close to the sources than remote ones; impacts due
to errors in simulating the above mentioned processes near
the sources would be most likely amplified during longrange transport. We therefore focus our present analysis
on AERONET data of the year 2000 from the African and
Middle East sites and exclude Caribbean-American stations
(Figs. S7 and S15 and corresponding figures in the Supplement). According to those figures the AeroCom median and
models ECMWF, SPRINTARS, LSCE and ECHAM5-HAM
underestimate the dust emissions in Africa while the CAM
model overestimate them in this region (Fig. 14a). For the
other models, either the AE was not available or the results
were not conclusive enough to propose an over/under estimation of the emissions. In the Middle East, the models LSCE
and ECHAM5-HAM underestimate the dust emissions while
models CAM, MATCH, MOZGN, UMI and SPRINTARS
overestimate them (Fig. 14b). Note that the analysis on the
Middle East is based only on the station at Solar Village.
This station has been documented as affected by dust particles from the deserts in the region (Sabbah and Hasan, 2008).
The regional emissions were computed for each model
(Table 5). The regions are illustrated in Fig. 2 and a few
models exist that consider desert dust sources outside these
regions. The models under/overestimating the emissions are
highlighted in blue/red in Table 5. When comparing the
emission fluxes between models it is important to consider
the simulated size distribution because coarse mode aerosols
will dominate the emission (in terms of mass) but will have
little impact on the AOD (at 550 nm) and conversely fine
mode aerosols will dominate the AOD (at 550 nm) but have
smaller impact on the emission mass. Furthermore, factors such as mass extinction efficiency (MEE) and aerosol
lifetime should also be considered when comparing emissions between different models. According to the results
in Fig. 14 and Table 5, SPRINTARS has larger emissions
than CAM in Northern Africa even though CAM overestimates the emissions in this region while SPRINTARS underestimates them. Although this might appear contradictory, it is consistent with the short lifetime of dust particles in SPRINTARS. According to its lifetime (1.6 days),
particles are removed shortly after emission and an important fraction probably even before arriving to the measuring site. The apparent underestimation is therefore consistent with the fact that particles are removed too fast from
the atmosphere. In the Middle East on the contrary, both
models (CAM and SPRINTARS) overestimate the emissions
suggesting that dust particles are transported to Solar Village
before their removal and thus overestimating the emissions.
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Table 5. Yearly emission fluxes [Tg yr−1 ] for regions illustrated in Fig. 2. Fluxes being overestimated are highlighted in red and those
underestimating are highlighted in blue. Models have been grouped according to their size ranges; models GISS to UMI simulate dust
aerosols in the size range 0.1–10 µm, models ECMWF and LOA in the size range 0.03–20 µm and UIO CTM in the range 0.05–25 µm.
Models LSCE, TM5, ECHAM5-HAM and MIRAGE describe dust aerosols through 1, 2, 2 and 4 modes respectively. For mass mean radius
and standard deviation of each mode see Table 1.
CAM
GISS
GOCART
SPRINTARS
MATCH
MOZGN
UMI
ECMWF
LOA
UIO CTM
LSCE
ECHAM5-HAM
MIRAGE
TM5
AEROCOM MEDIAN
North Africa
Middle East
Asia
South America
South Africa
Australia
North America
2271
1031
1736
2888
539
1410
933
204
772
1213
529
401
703
1091
792
526
125
348
531
241
376
329
68
114
206
39.2
25.6
292
212
128
727
180
873
363
100
294
340
125
411
27
509
54
608
253
137
13.7
39.9
66.5
6.9
19.3
92.8
47.1
1.0
0.5
5.0
0.2
3.7
186
30.4
9.8
2.9
31.7
25.0
113
24.5
55.4
20.6
16.3
3.5
11.6
57.2
40.2
25.0
15.3
11.8
12.2
87.8
111
36.8
40.9
89.5
35.4
57.0
14.9
9.0
10.6
58.4
129
59.4
30.7
286
7.3
13.0
4.1
2.4
12.7
6.1
15.3
4.5
1.8
7.2
1.7
70.8
8.1
2.0
We decide to exclude SPRINTARS from the following analysis in view of the uncertainty in the emissions associated
to a short lifetime. Based on the above results we suggest
that a range of plausible emission for North Africa is 400 to
2200 Tg yr−1 while in the Middle East the range of plausible
emissions is between 26 and 526 Tg yr−1 . We note however
that emission fluxes outside these ranges can be possible depending on the definition of parameters such as size distribution, lifetime and MEE.
4.4
AFRICA
MIDDLE EAST
General discussion
Because there was no AERONET station affected by the
Asian dust sources which met the criteria used in this study,
we could not evaluate the performance of the models in simulating the dust cycle in Asia. Months with intense dust activity were masked by anthropogenic emissions which generated AE values above 0.4 and therefore were not recognisable with our definition of dust sites. However, surface concentration measurements in Midway in the Northern Pacific
(station 15 in Fig. 2) and Hedo and Cheju (stations 20 and 22
respectively in Fig. 2) in eastern Asia, even though limited,
give us some insight in the general model performance in
simulating the Asian dust. As described in Sect. 3.2, in general the models reproduce annual cycles in these sites mostly
underestimating the observations in Hedo and Cheju while in
Midway the models mostly underestimate the observations in
spring and overestimate them in months following the spring
peak. A few models exist that largely overestimate the surface concentration at these sites. In periods of maximum conAtmos. Chem. Phys., 11, 7781–7816, 2011
Fig. 14. Suggested resulting over/under estimation (EMI) of the
emissions in Africa (left panel) and the Middle East (right panel)
based on AERONET Angström Exponent (AE) and aerosol optical
depth (AOD). Simultaneous overestimation of the AOD and underestimation of the AE suggests an overestimation of the emissions
and vice versa. Overestimations in a given model are illustrated by
red color, whereas underestimations are indicated by blue color.
centrations the simulated values of a large number of models
is within the observed variability (Fig. 15). The differences
between models and observations however could be due to
the nature of the data; they are considered as climatology in
this study even if they do not qualify for it in a strict sense
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Fig. 15. Measured and simulated surface concentration in the Asian stations of Hedo and Cheju and the Pacifica station in Midway Island.
Measurements are presented by the black continuous line. Units are µg m−3 .
and the measurement period does not coincide with the year
simulated. In addition, the comparisons of surface concentrations at stations affected by Saharan (Barbados, Bermuda
and Miami) and Asian dust (Hedo, Cheju and Midway) reveal that in general models have not only smaller biases and
errors when reproducing the annual cycle at Asian stations
but also present smaller model diversity. This in spite of the
fact that dust emissions in global models are generally tuned
to fit the observations in a given part of the world and often
this tuning is done with observations from North Africa. Because we have no AOD and AE data for the Asian deserts
and because of the climatological aspect of the surface concentration data, we cannot assess whether this difference in
performance is also observed in other aspect of the dust cycle. A more specific Asian dust data set is needed to address
this issue and examine the role of the tuning in the performance of global dust models. We therefore excluded Asia
from this study. One way to assess the performance of global
dust models over Asia would be to compare measurements
of coarse mode AOD against modelled ones.
The models perform better (smaller errors and biases) in
simulating the climatology of vertically integrated variables
in dusty sites than they do with deposition and surface concentration measurements. The modeled AOD is within a
twofold range of the observations at most sites, whereas
model under/overestimations of surface concentrations and
total deposition are more typically within a range of a factor of 10. Differences in the data can explain this since
the AERONET climatology includes the simulated years
whereas the deposition and surface concentration climatology do not. The surface measurements were considered as
climatology in this study although, in a strict sense of the
term, they were not. Furthermore, surface concentration and
deposition require that the model correctly simulates the vertical distribution whereas for vertically integrated parameters
such as AOD and AE the vertical distribution is less relevant (assuming that they are clear-sky measurements of nonhygroscopic particle such as dust). In addition, this difference in performance might also suggest that AeroCom models (as used in experiment A) are more adequate to assess
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the radiative impact of dust aerosols than their impact on air
quality and/or the biogeochemical cycle.
Throughout the text when comparing the models to each
variable and in the consequent analysis, we treated the AeroCom median as any other model even though it is not a
real one but a construction from multiple state-of-the-art AeroCom A models. For the integrated variables of AOD (for
the year 2000) and AE (year 2000 and climatology) the AeroCom median is among the models with the smallest MNB
and NMRS, in some cases even the one with the smallest
value. Both MNB and NRMS correspond to the analysis of
the averaged values and therefore do not reflect the model
performance on the annual cycle. These AeroCom statistics
suggest that random error might cancel out when computing
the median. By construction, the AeroCom median has the
same deficiencies present in most models such as the difficulties to reproduce the fraction of wet deposition when dry
deposition dominates and to simulate the transport of Saharan dust to Surinam in northern South America during winter
months.
This is the first multi-parameter and multi-model intercomparison of global dust models. Fifteen models from the
AeroCom project have been compared to different and multiple datasets. The models were examined in their performance to simulate surface variables such as deposition and
dust concentration and the vertically integrated variables of
AOD and AE. A recurrent problem when evaluating the performance of a dust model is the data available to do it. A
benchmark dataset has been created containing all the information used in this work and available through the AeroCom
data server. There are various datasets that have been used for
model evaluations (e.g. Prospero et al., 2010; Prospero and
Lamb, 2003; Ginoux et al., 2001; Mahowald et al., 2009; and
the DIRTMAP data set). These studies concentrated mostly
on a single parameter. We have grouped in a single database
the data used in these studies to ease future comparison and
evaluations.
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To further improve this benchmark dataset, additional deposition and surface concentration measurements are needed.
Long term measurements of total and wet deposition are
required, in particular over remote regions in the Southern
Hemisphere where the greatest model diversity is observed
and where the role of the atmospheric iron in the ocean biogeochemistry is still under debate (Jickells et al., 2005). With
respect to surface concentration, additional surface concentration measurements are needed such as the ones taken during the SEAREX and AEROCE campaigns and those still
being measured at Barbados and Miami. Since AOD is dominated by the fine mode due to its higher extinction efficiency
and since the coarse mode dominates the surface concentration and deposition, it is important that future measurements as well as model simulations deliver size-resolved information. The absence of this information, in both data
and model, prevented us from gaining more insight on the
model performance and identifying the possible role of the
size distribution in models in the over- and under-estimation
of deposition and surface concentration. The AERONET network represents a crucial source of data in validating models. The information of this network should be complemented with satellite products to further evaluate the model
performance. The contribution of vertically resolved active measurements from the in-situ Micro-Pulse Lidar Network (MPLNET) and/or from the remote sensor Cloud and
Aerosol Lidar with Orthogonal Polarization (CALIOP) onboard the Cloud-Aerosol Lidar and Infrared Pathfinder Satellite Observations (CALIPSO) would provide valuable information on the vertical distribution of dust aerosols. This information would provide additional constrain to model evaluation and would allow to assess and understand present difficulties to simulate surface variables.
5
Conclusions
Desert dust plays an important role in the climate system
through its impact on the earth radiative budget and its role
in the biogeochemical cycle as a source of iron in highnutrient-low-chlorophyll regions. However, there are large
differences in the way many global models simulate the dust
cycle and the resulting impact of dust on climate. On the
one hand, these differences are the product of the various
distributions in dust burden and aerosol optical depth which
translate into uncertainties in the estimation of the direct radiative effect (Textor et al., 2006; Forster et al., 2007). On
the other hand, they result from differences in simulated dust
deposition fluxes, which prevents one from properly estimating the impact of dust on ocean CO2 uptake in HNLC regions
(Textor et al., 2006; Tagliabue et al., 2009).
Here we present the results of the first multi-parameter and
multi-model intercomparison of a total of 15 global aerosol
models within the AeroCom project. Each model is compared to the same set of observations, focusing on variables
Atmos. Chem. Phys., 11, 7781–7816, 2011
that have a direct link to the estimation of the direct radiative
effect and the dust impact on the biogeochemical cycle, i.e.
aerosol optical depth (AOD) and dust deposition. To extend
the assessment of model performance we include additional
comparisons to Angström exponent (AE), coarse mode AOD
and dust surface concentration. Altogether these comprise a
new benchmark data set which is available via the AeroCom
data server for model inspection and future development of
dust models.
Note that the model results used in the present analysis
correspond mostly to a coherent set of AeroCom simulations
submitted before the year 2005. Many of these models have
been changed and are likely improved since submitting their
simulations. Therefore the results presented in this study do
not necessarily represent the current state of the models.
The models simulate the yearly dust deposition within a
factor 10 with respect to the observations. While the deposition is mostly overestimated in Europe, North Atlantic and
the Indian Ocean, it is mostly underestimated in the Pacific
and South Atlantic Ocean. The limited number of deposition
data in HNLC regions and the dependence of the models performance in simulating these data to the location of the data
prevent us from concluding on the atmospheric iron contributions in HNLC regions from global dust models. Further
measurements and model studies are necessary to address
this issue and to assess whether the impact of dust on the
ocean biogeochemical cycle in the southern ocean is over- or
under-estimated in most models.
In terms of wet and total deposition, models capture the
seasonality of the deposition and the dominance of wet over
dry deposition in Florida but most underestimate the magnitude. Furthermore, the performance deteriorates from south
to north Florida, reflecting difficulties in reproducing the
northward dust transport. Data on wet deposition fraction
shows that models manage to reproduce the fraction of wet
deposition in regions where the wet deposition dominates but
fail to do so in sites dominated by dry deposition. Long-term
measurement records are needed, ideally on a daily basis and
over oceans, to evaluate model ability to reproduce the deposition fluxes. While it is relatively easy to collect and measure wet deposition, there is no easily implemented technique
for measuring dust dry deposition to natural surface, in particular the ocean. Thus it is unlikely that we will soon be
able to test model dry-deposition simulations in a meaningful way.
The model performance in simulating surface concentration depends on the database used. All models mainly overestimate the surface concentration measured during cruise
campaigns mostly by a factor of ten up to a hundred. When
using long-term measurements, on the other hand, the overestimations are within a factor of ten with respect to the observations. If the sampling error of missing dust events during short-term cruise measurements is taken into account the
large overestimation is reduced and the performance resembles the one observed with long-term measurements. Despite
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N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
this large uncertainty, surface observations deliver valuable
information in remote regions of the Southern Oceans and
South Atlantic Ocean where data are scarce. For both
datasets, cruise campaign as well as long-term, all models
underestimate the surface concentration within a factor of ten
with respect to the observations.
Model performance is better at sites with a large range
of measured surface concentrations, reflecting better agreement at stations directly downwind of the main sources than
at those in remote regions. The transatlantic dust transport,
captured by stations on both sides of the Atlantic, is reproduced by most models. The models coincide in the onset of
the period of maximum surface concentration. However they
differ in simulating the magnitude of the measurements in
this period and its extension in time. For the Pacific stations
exposed to Asian dust, most models simulate the general seasonal variations underestimating the observation in months
with maximum surface concentration.
A similar conclusion on the regional performance of the
models, not contradictory to the above, can be reached based
on comparison to the sun photometer data. The models simulate in general the gradient in AOD and AE between the
different dusty regions. However the models show less skill
in reproducing the magnitude and seasonality in the Middle
East of both AOD and AE. Model performance in reproducing Asian dust could not be explored due to the definition
of dusty sites used in the study; months with intense dust
activities co-incided with AE values above 0.4, influenced
by anthropogenic emissions, were masked out. A different
selection criteria or approach would be needed to examine
the performance of global dust models in this region. Like
for surface concentrations, the models reproduce the transAtlantic dust transport from the Sahara in terms of AOD and
AE. All models reproduce the offshore transport of Saharan
dust throughout the year as revealed by data from Capo Verde
offshore western Africa. Also they limit the transport across
the Atlantic to the Caribbean to the summer months in agreement with measurements at Barbados and Roosevelt Roads,
Puerto Rico; however they overestimate the AOD and they
transport too fine particles. In contrast, almost no model reproduces the southward displacement of the trans-Atlantic
Saharan dust plume during the Winter and Spring as captured
by the AOD and AE data at Surinam, which are representative of the dust transport into South America and which has
been well documented by various satellite products and by
ground-based aerosol measurements.
Models perform better in simulating the climatology of
averaged vertically integrated parameters (AOD and AE) in
dusty sites than total deposition and surface concentration reflected by smaller MNB and NRMS for AOD and AE than
for surface variables. The averaged AOD and AE are within
a factor of two of the observations at most sites; in contrast
the long-term surface concentrations and total deposition are
under- and over-estimated within a factor 10 of the observations. This difference might be explained by the different
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7811
characteristics of the data climatologies used, as well as the
simulated vertical structure important for reproducing dust
deposition and surface concentration.
Based on the dependency of AOD and AE on aerosol burden and size distribution we use the simultaneous overestimation or underestimation of AOD and underestimation or
overestimation of AE to suggest whether a model is overestimating or underestimating dust emissions. Note, that if
AOD and AE bias in a given model is of equal sign then
no conclusion with respect to emissions can be made. From
this analysis we suggest that the AeroCom median model and
models ECMWF, LSCE and ECHAM5-HAM underestimate
the emissions in Africa while CAM overestimates them. In
the Middle East the models LSCE and ECHAM5-HAM underestimate the emissions, whereas models CAM, MATCH,
MOZGN and UMI overestimate them. According to these results we suggest that a range of possible emissions for North
Africa is 400 to 2200 Tg yr−1 and in the Middle East 26 to
526 Tg yr−1 . Emission fluxes outside these ranges might be
possible however depending on the definition of relevant parameters.
The AERONET data and satellite products are important
data sources in aerosol model evaluation, but need to be complemented with deposition data in order to properly evaluate
the overall dust cycle included in models. Dust deposition
measurements are sparse and deliver mostly only total deposition fluxes for a given event or a longer time period not necessarily coincident with the year simulated, thus limiting the
model evaluation. The proper testing of models requires the
permanent monitoring of dust deposition in a manner similar
to that in the network presented in Prospero et al. (2010) and
of dust concentrations (Prospero and Lamb (2003).
The new round of experiments conducted within AeroCom
Phase II with additional diagnostics, including a multi-year
hindcast with observed meteorology, will allow conducting
further comparisons to assess the model performance to simulate the dust cycle. Notably, the detailed size distribution information stored in the new experiments will allow addressing issues such as the impact of the simulated size distribution in reproducing the deposition flux and surface concentration. This information was not available from experiments
A and B from the Phase I of AeroCom and prevented us from
addressing the role of size in explaining the different model
performances in reproducing the deposition and surface concentration. In addition to archiving the size-resolved surface
concentration and deposition, we recommend also archiving
concentrations above the surface at a few locations in order
to allow comparisons in elevated mountain stations. In order
to further evaluate the model performance, the AERONET
data should be complemented with satellite products, notably
the vertically resolved information provided by CALIOP and
MPLNET.
Atmos. Chem. Phys., 11, 7781–7816, 2011
7812
N. Huneeus et al.: Global dust model intercomparison in AeroCom phase I
Supplementary material related to this
article is available online at:
http://www.atmos-chem-phys.net/11/7781/2011/
acp-11-7781-2011-supplement.pdf.
Acknowledgements. The authors would like to thank two reviewers for their useful comments that contributed to improve
the manuscript. In addition we thank the AERONET program
for establishing and maintaining the used sites. This study was
co-funded by the European Commission under the EU Seventh
Research Framework Program (grant agreement No 218793,
MACC). O. Boucher was supported by the Joint DECC and Defra
Integrated Climate Programme, DECC/Defra (GA01101). S. Ghan
and R. Easter were funded by the US Department of Energy, Office
of Science, Scientific Discovery through Advanced Computing
(SciDAC) program and by the NASA Interdisciplinary Science
Program under grant NNX07AI56G. The Pacific Northwest
National Laboratory is operated for DOE by Battelle Memorial
Institute under contract DE-AC06-76RLO 1830.
Edited by: M. Kanakidou
The publication of this article is financed by CNRS-INSU.
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