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Vol.21 No.11
Aerobiology and the global transport
of desert dust
Christina A. Kellogg and Dale W. Griffin
US Geological Survey, 600 4th St S, St Petersburg, FL 33701, USA
Desert winds aerosolize several billion tons of soilderived dust each year, including concentrated seasonal
pulses from Africa and Asia. These transoceanic and
transcontinental dust events inject a large pulse of
microorganisms and pollen into the atmosphere and
could therefore have a role in transporting pathogens
or expanding the biogeographical range of some organisms by facilitating long-distance dispersal events. As
we discuss here, whether such dispersal events are
occurring is only now beginning to be investigated.
Huge dust events create an atmospheric bridge over
land and sea, and the microbiota contained within them
could impact downwind ecosystems. Such dispersal is
of interest because of the possible health effects of
allergens and pathogens that might be carried with
the dust.
Introduction
Dust clouds generated by storm activity over arid lands can
result in soil particulates being transported to altitudes
>5 km [1]. The Sahara–Sahel region of Africa is the largest
source of aerosolized soil dust on Earth, contributing as
much as one billion metric tons of dust yr 1 to the global
atmosphere [2]. Deserts continuously discharge dust, but it
is the large-scale dust events, visible from space and capable
of crossing oceans (Figure 1), that could have the biggest
impact on the biology and ecology of downwind ecosystems.
The intercontinental transport of African desert dust has
been studied for decades [3], but, as we discuss here,
research on the biological particles traveling between continents with the dust has only recently been initiated
(Table 1). The topic has generated interest because of
concerns about health effects of allergens carried in the dust
[4–6] and the possible transport of pathogens [7].
Dust (and biology) in the wind
Several mechanisms contribute to the microbial load of
African desert dust, in addition to the 106 bacteria g 1 of
soil estimated to occur naturally [8]: as they move across
the continent, local winds lift large quantities of arid soil.
Garbage disposal in many parts of Africa is accomplished
by burning [9], which can contribute bacterial and fungal
spores in the rising smoke [10]. Finally, the trade winds
blow the dust out over the Atlantic Ocean, where additional marine microorganisms aerosolized by wave action
can be picked up.
Corresponding author: Kellogg, C.A. (ckellogg@usgs.gov)
Available online 14 July 2006.
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Wind-borne bacteria are typically transported <1 km
from their source [11], however, dust-associated bacteria
can be transported over 5000 km from Africa to the
Caribbean [12,13]. Fungal spores and pollen are adapted
for aerosol dispersal and can be transported thousands of
kilometers in the presence or absence of dust [14]. Satellite
images show that African dust is regularly transported
west over the Atlantic Ocean to the Americas and
Caribbean, as well as north over the British Isles to
Scandinavia, across the Mediterranean to Europe, and
into Southwest Asia (Figure 1). Similarly, Asian dust from
the Takla Makan and Gobi deserts is blown eastward
across Korea, Japan and the Pacific Ocean, affecting the
Arctic, Hawaiian Islands and the west coast of the USA
(Figure 2) [15]. Some exceptionally large dust events, such
as the Asian dust storm that occurred during April 2001,
can circumnavigate the northern hemisphere. The
southern hemisphere is affected by Australian dust, which
is deposited into the Tasman Sea and on New Zealand
(Figure 2) [16].
These intercontinental dust events can facilitate
long-distance dispersal (LDD) of dust-associated biological
particles. The surprising lack of research into microbial
LDD by dust is partly due to a common misconception
that all microorganisms in dust clouds are killed by solar
UV-radiation, lack of nutrients and desiccation during
their multi-day journey. In fact, some genera of bacteria
(e.g. Bacillus) and most fungi can form spores, a dormant
state that is resistant to desiccation, heat, radiation and
nutrient-poor conditions [17]. Many of the bacteria that are
isolated from aerosol samples are highly pigmented, suggesting that pigmentation also helps shield the microbes
from UV radiation [9,18,19], in addition to the protection
afforded by clouds, fog, smoke and desert dust particles.
The length of time spent in the atmosphere and the distance traveled varies, but what goes up must come down.
Microbes, pollen and mineral dust particles are eventually
removed from the atmosphere by gravity or precipitation
[20,21].
Evidence for LDD of microbiota via dust events
There is no doubt that microbes and pollen are contained
within these large desert dust events; however, only
recently have data been presented that implicate these
dust events as mechanisms for transporting aerosolized
microbiota around the globe. These data come from
satellites and classical microbiology and molecular biology
studies.
0169-5347/$ – see front matter ß 2006 Elsevier Ltd. All rights reserved. doi:10.1016/j.tree.2006.07.004
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TRENDS in Ecology and Evolution
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used to track pulses of African dust during concurrent
microbiological aerosol sampling [12,18,24]. At present,
desert dust visualized by satellite imagery is used as a
proxy for microbes and pollen, providing an indirect estimate of the geographical range of possible dispersal events.
However, remote-sensing tools are being developed to
model or monitor microbes directly in the marine environment (Box 1), and these tools could be adapted to monitor
aerosolized microbes.
Figure 1. The intercontinental dispersal of African desert dust. Most of the dust
moves westward in pulses from the Sahara–Sahel to the Caribbean and Americas,
as shown in (a) and (b): (a) dust pours off the northwest African coast and blankets
the Canary Islands,11 February, 2001; (b) a dust cloud covering the entire Caribbean basin, 28 May, 1999. However, it is not unusual for dust from northern Africa to
blow east into Europe and the Mediterranean as shown in this image from 13
October, 2001 (c). Less frequently, winds carry Saharan dust north over the British
Isles, as on 13 February, 2001 (d). (a,c,d) reproduced with permission from the
SeaWiFS Project, NASA Goddard Space Flight Center, and ORBIMAGE. (b) is an
enhanced GOES 8 satellite photo reproduced with permission from NOAA.
Satellite data
Images from the Sea-viewing Wide Field-of-view Sensor
(SeaWiFS), carried by the OrbView-2 satellite, enable
pulses of desert dust to be visually traced from their source
to thousands of kilometers downwind (Figure 1a,c,d).
These images document the huge mass of particulates
(including bioaerosols) being ejected into the atmosphere;
an image captured on February 26, 2000, of an African dust
event the size of Spain precipitated commentary online, in
the popular press, and in scientific articles (e.g. [22]).
Images from the Earth Probe-Total Ozone Mapping
Spectrometer (TOMS) provide measurements of global
aerosols [23]. TOMS aerosol data are currently being
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Enumerating dust-associated microbes
Only eight recent publications have investigated desert
dust-associated microbes after long-distance transport,
plus one additional study conducted in a desert source
region specifically for comparison (Table 1). These papers
address both the African and Asian dust systems (Figure 2)
but a lack of standard methodology (Box 2) makes it
difficult to compare results between or within systems.
Different approaches have been applied to answer different
questions as the focus of studies varies from allergens
[5,6,25], to coral pathogens [26] and characterizing the
dust-associated microbial community [12,13,18,24,27].
These studies all conclude that there are dustassociated microbes in that there are higher concentrations of aerosolized microorganisms during dust events.
However, the magnitude of the concentrations and the
specific microbes associated with the dust events remain
topics of debate. As Table 1 shows, there are a wide range of
values for concentrations of dust-associated microorganisms. A large part of the variability is due to the different
collection methods; cultivation-independent methods, such
as spore traps (which capture the fungal spores on an
adhesive surface for counting by microscopy), will always
generate higher counts than will a culture medium which
selects for the subset of microorganisms capable of growing
on it (Box 2). Additionally, numeric and taxonomic differences between samples might be due to heterogeneity or
patchiness in the distribution of the microbial community
within the dust event; for example, during dust events, the
concentration of microorganisms (i.e. bacteria and fungi)
does not correlate with the concentration of mineral dust
particles [12].
Dust-associated fungi
Even when two research groups used the spore trap
method to examine Asian dust at two different cities in
Taiwan, the results were different [5,6]. Wu et al. [6] found
no statistically significant difference between the concentration of fungal spores in dust versus background samples
in Tainan City, but did note that some types of fungi
(Basidiospores, Aspergillus, Nigrospora, Arthrinium and
Curvularia; rusts, Stemphylium, Cercospora, Pithomyces
and unidentified fungi) were between two and 12 times
more abundant during dust events. Conversely, Ho et al.
[5] found significantly higher total fungal spores associated
with dust events ( p < 0.05) in Hualien City, and different
genera of fungi that occurred at higher concentrations
during dust events (Cladosporium, Ganoderma,
Arthrinium/Poularia, Cercospora, Periconia, Alternaria
and Botrytis). The findings that Periconia and Botrytis
concentrations were significantly higher during dust events,
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Table 1. Comparison of dust-associated microbe studies
Dust system:
approx. distance
from source region a
African (0 km)
Microbes
Collection
method
Analysis b
Bacteria;
fungi
Filtration
African (5500 km)
Bacteria;
fungi
Bacteria;
fungi
Filtration
Culture,
DNA sequencing of
isolates
Culture, microscopy
African (6000 km)
Filtration
Fungi
Filtration
Asian (2600 km)
Fungi
Asian (2700 km)
Bacteria;
fungi
Fungi
Impaction;
filtration
Impaction
Spore trap
Culture, DNA
sequencing of
isolates
Culture, microscopy,
DNA sequencing of
isolates
Culture, microscopy
Culture
Microscopy
Concentration of aerosolized
microbes during dust event
(range or average)c,d
720–15 700 bacterial CFU m 3
80–370 fungal CFU m 3
Concentration of aerosolized
microbes during background
conditions (range or average) c
200–1100 bacterial CFU m 3
0–130 fungal CFU m 3
Refs
0–20 bacterial CFU m 3
0–16 fungal CFU m 3
90–350 bacterial CFU m 3
30–60 fungal CFU m 3
0–185 bacterial CFU m 3
0–90 fungal CFU m 3
50–83 fungal CFU m 3
0 bacterial CFU m 3
0 fungal CFU m 3
100 bacterial CFU m 3
60 fungal CFU m 3
0–66 bacterial CFU m 3
0–40 fungal CFU m 3
0–50 fungal CFU m 3
[12]
Not quantified
Not quantified
[25]
105–621 bacterial CFU m 3
100–5929 fungal CFU m 3
28 684 fungal spores m 3
4839 fungal spores m 3
[27]
225–3426 bacterial CFU m
336–2692 fungal CFU m 3
29 038 fungal spores m 3
6078 fungal spores m 3
3
[18]
[24]
[13]
[26]
[6]
[5]
a
Distances were estimated between West Africa, the Virgin Islands, and Barbados; and the Gobi desert, South Korea, and Taiwan using http://www.mapcrow.info.
DNA sequencing indicates partial sequencing of the 16S rDNA gene in bacteria and the 18S rDNA gene in fungi for identification.
Averages are provided when ranges could not be determined from the data.
d
CFU, colony forming units, assumed to have originated from a single bacterium or fungal cell.
b
c
whereas Curvularia and Pithomyces were significantly
higher during background conditions, are the reverse of
the findings of Wu et al. These differences were attributed
to regional geographical differences and weather conditions in that Tainan is on the west coast of Taiwan facing
China, whereas Hualien is on the east coast, requiring that
dust travel over Taiwan to reach it.
All nine studies (Table 1) agree that the composition of
the aerosolized microbial communities varies dramatically
during dust events and consist of a greater number of taxa
Figure 2. Principal ranges of the two major global dust transport systems. The African dust system (red–orange) has a strong seasonal component; in the summer
(c. May–November) trade winds carry Saharan dust to the Caribbean and USA. In the winter (c. December–April) the African dust-flow is shifted to South America, where
air-plants in the Amazon rainforest derive nutrients from the dust. Throughout the year, pulses of dust from northern Africa cross into the Mediterranean and Europe,
impacting air quality. The Asian dust system (yellow) exports dust primarily during the spring (March–May). These dust events can incorporate emissions from factories in
China, Korea and Japan, carrying a ‘brown smog’ across the Pacific to the west coast of North America. Occasionally, extremely large Asian dust events can travel across
the entire USA and then impact Europe, making an almost complete circuit of the globe. Although not an intercontinental dust source, Australian deserts (pink) produce
large dust storms that can reach New Zealand and halfway to South America. This updated version of a figure from [9] is reproduced with permission.
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Box 1. Applying satellites to microbial ecology
Box 2. The need for standardized methods
Remote sensing, the use of satellites to monitor processes on
broader regional scales, is being applied to microorganisms
[52,53]. Most satellite methods involve using a proxy, such as sea
surface temperature (SST), sea surface height (SSH), ocean color,
and so on, to track the microorganisms. For example, Vibrio
cholerae concentrations in the marine environment correlate very
closely with temperature. The bacteria also are closely associated
with marine plankton, and SSH is a good indicator of incursions of
plankton-rich waters into near-shore bays. By combining satellite
data on SST and SSH, a statistically significant correspondence can
be made with the incidence of cholera in Bangladesh [54]. Thus,
satellite data can be used to estimate the location and concentration of V. cholerae as well as to predict areas of cholera outbreaks.
There are rare examples of more specific detection, mainly of
marine phytoplankton, which can be detected by algorithms based
on multiple color bands that distinguish the unique fluorescence
spectra of the photosynthetic pigments of the microorganism
[55].
It has been suggested that aerobiological dispersal processes (for
organisms as diverse as birds, insects, viruses, bacteria, fungi,
pollen and seeds) can be studied by an ecological scaling approach.
That is, examining dispersal events as they relate to larger
geographical areas and time scales, for example by utilizing
topographic maps and satellite data of vegetation change [56].
Many of the factors that affect atmospheric microbial transport and
survival, such as temperature, humidity, precipitation and wind
strength and direction can be monitored by existing meteorological
and satellite systems [53]. As more types of sensors become
available and microbiologists provide a better understanding of
how individual microbial species are affected by environmental
parameters, the current framework can be expanded to use these
global tools to better study the phenomenon of long-range
microbial dispersal in the atmosphere.
Many dust-related studies (Table 1, main text) use culture-based
analyses to isolate microorganisms not only because culturing is
relatively easy and inexpensive, but also because it was of interest
to show that microbes were viable after being transported several
thousand kilometers, and therefore capable of causing an infection
or establishing a niche in downwind environments. Culturing a
microbe also enables additional assays to characterize its biochemical and physiological capabilities (e.g. antibiotic resistance
profiles, [18]). However, the use of diverse culture media (e.g. R2A,
blood agar, malt extract or potato dextrose) renders many of the
culture enumeration data non-comparable. Each type of nutrient
agar creates a slightly different selection bias, and even if the
bacterial and fungal counts are identical between agars, counts
can represent a different mixture of species. R2A, a low-nutrient
agar designed to cultivate stressed heterotrophic bacteria from
water and which has been used in several aerobiology studies
[13,18,20,24,57], is recommended as a standard general medium.
Enumeration of dust-associated fungal colonies on R2A resulted
in counts that did not significantly differ from those of identical
samples grown on malt extract agar and Sabouraud’s agar
[12,18].
It is also necessary to determine standard methods of collection
and molecular analysis to reveal the true diversity in microbial
aerosol communities. Only 1–10% of environmental bacteria are
culturable on any given medium [58]; culture-independent methods
provide access to the viable-but-not-culturable bacteria, as well as
fungi, archaea and viruses that are presently not detected in dust
events. Microbial-community DNA extraction followed by the
creation of 16S rRNA gene sequence libraries has been accomplished with non-dust aerosol samples [59,60] and it is expected that
data of this type will shortly be generated from dust-events.
However, collection methods do differ: one study used a filtration
system and then extracted DNA from the filter [60], whereas the
other utilized a liquid impinger system where the aerosol particles
were trapped in a liquid buffer [59]. Capturing bioaerosols in a liquid
medium simplifies division of the sample, which can then be
analyzed by multiple methods, including culture, direct DNA
extraction, and enumeration by microscopy [61].
than do the background samples. In several of the studies
[5,6,13,18,24], Cladosporium was the numerically dominant fungal genus detected during dust events; however
this could be because Cladosporium is both ubiquitous and
commonly found in aerosol samples [28]. Aspergillus species were also found to be associated with dust events
[6,12,13,18,25,26]. Although this genus is also frequently
observed in aerosol samples, the species are of interest
because of their roles as allergens, and in one case
(Aspergillus sydowii), as a coral pathogen [26].
background and dust conditions in the Caribbean. Total
bacterial counts from these same filters were almost identical to the viral counts. This was surprising because, in
soil and marine environments, there are typically an order
of magnitude more viruses than bacteria (in those cases,
most of the particles are bacteriophages, or bacterial
viruses). It might be that fewer viral particles are able
to survive the high UV radiation and dry air associated
with long-distance transport in dust events.
Dust-associated bacteria
Four studies of African dust identified bacterial isolates
[12,13,18,24]. Most of the bacteria are Gram positive, and
many are spore-formers, making them more resistant to
desiccation. It is possible that the filtration methodology
used in these studies has a selection bias for desiccationresistant microbes, however, these are the types of
microorganism that are most likely to survive transoceanic
transport in a dust event. Bacillus [12,13,18] and
Microbacterium [13,24] were the numerically dominant
genera of bacteria isolated.
Dust-associated pollen
A recent study investigated pollen transported from North
Africa to Spain via Saharan dust, and found that pollen for
five species of non-native plants were exclusively detected
during dust events [29]. In another study, exotic Casuarina
pollen found in New Zealand peat and soil samples is
believed to have been deposited via atmospheric transport
from Australia [30].
Dust-associated viruses
To our knowledge, there is only one study that mentions
virus-like particles being associated with a transoceanic
dust event [24]. This report is based on epifluorescent
microscopy of filters stained with a nucleic-acid specific
stain. An order of magnitude increase in virus-like particles, from 104 m 3 to 2.105 m 3 was observed between
DNA sequence evidence of LDD
Although the increased number and taxa of microorganisms
detected during dust events is indicative of a dustassociated microbial load, it is still difficult to determine
specifically which microorganisms arrived with the dust
and which were present in the local atmosphere. The main
problem is insufficient identification. Many of the studies
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were limited to the genus-level identifications possible by
microscopy. However, microbial biogeographical distinctions require identifications to the species or even strain
level [31]. Four studies identified some of their cultured
isolates by partial sequencing of the 16S rRNA gene (bacteria) and 18S rRNA gene (fungi) [13,18,24,26]. Comparisons between these small sample sets show that 19
bacterial isolates from dust events sampled in the Caribbean were of the same genus and species as isolates from
dust events sampled in an African source region [18,24].
Comparison of 16S sequences between Caribbean and
African samples revealed that there was one bacterium
(Kocuria erthyromyxa) with 100% sequence identity,
and another (Bacillus pumilus) with 99% identity [18].
Comparing fungal isolates, 18S sequences for all four of
the Cladosporium isolates from the Caribbean samples
were 99–100% identical to an isolate from dust samples
collected in Africa [18]. However, it has recently been
shown that bacteria with identical 16S sequences can have
significant differences in their genome and physiological
capabilities [32]. Therefore, although these genetic similarities are suggestive of LDD from Africa to the Caribbean,
our limited understanding of microbial biogeography
makes these data preliminary at best.
Consequences of the LDD of desert dust
Interest in the LDD of desert dust has been increasing as
questions have arisen about the potential effects of associated chemical pollutants and pathogenic microbes on
human health and ecosystems [9,33,34]. Recent work in
this area raises issues of pathogen transport and the
biogeography of microbes and pollen.
Transport of pathogens
There are economic and agricultural concerns raised by the
possibility of intercontinental dust events enhancing the
spread of plant and animal diseases. The limited genetic
diversity of many modern crops increases the risk that
a disease outbreak could quickly achieve worldwide
distribution given that many of the plants are clones with
identical susceptibility [35]. Of the microorganisms
identified from African dust aerosols in three studies,
5–25% have the potential to be plant pathogens; that
is, the genus or species identified is known to contain
members that cause disease [13,18,24]. Examples include
Bacillus pumilus, which can cause bacterial blotch
in peaches, and Bacillus megaterium, which can cause
‘wetwood’ disease in trees.
Transoceanic or intercontinental aerosol transmission
of a livestock pathogen has not yet been reported.
However, there have been reports of the foot-and-mouth
disease virus (FMDV) being transmitted by aerosols from
Germany to Scandinavia, and from France to England
[36,37], which led to speculation that FMDV could be
carried from Africa to Britain or South America via desert
dust [38]. It has also been suggested that FMDV has
traveled from China to Korea in Asian dust [33].
A hypothesis has been offered that infectious agents in
African dust could be linked to widespread episodes of
coral reef morbidity and mortality occurring across the
Caribbean basin [7]. This hypothesis has been supported
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by the discovery of the fungus Aspergillus sydowii, causative agent of sea fan aspergillosis, in Sahelian soil [39]
and African dust events sampled in the US Virgin Islands
[26].
Although opportunistic human pathogens, such as
Aspergillus fumigatus, Aspergillus niger, Staphylococcus
gallinarum and Gordonia terrae, have been identified in
African dust [12,13,18,24], there are no reports as yet of
human infectious diseases related to LDD of desert dust.
However, correlations between African dust events and
increased incidences of asthma in the Caribbean have been
proposed and confirmed [40,41].
Biogeographical patterns of microbial diversity
Microbiologists have been arguing for over 70 years about
whether microbes exhibit biogeographical patterns [42,43].
The historical view, dating back to the early 1900s, is
summed up by a quote attributed to Martinus Beijerinck:
‘Everything is everywhere, the environment selects’ [44].
The assumption is that microorganisms must have a cosmopolitan distribution owing to their enormous population
sizes and ease of dispersal and, therefore, the microbial
species found in a given habitat are a function of the
selective properties of that environment and have no
link to historical factors (e.g. previous desert dust events)
[44]. Although there is evidence supporting this view
[44], the idea presupposes (i) successful dispersal; (ii)
successful colonization, and (iii) survival, none of which
are guaranteed [45,46]. For example, spore-formers, such
as Bacillus spp., are more likely to survive long-distance,
dust-associated dispersal than are many Gram negative
bacteria and, accordingly, are among the most commonly
isolated genera in downwind dust samples [12,18].
Invasion or colonization capabilities will thus vary by
species if not by strain.
Evidence of geographically distinct microbial populations has been offered: a study of fungi in Australian desert
soils demonstrated that genetic divergence between fungi
from different locations increased with the geographical
distance between them [43]. In another study, strains of
Sulfolobus islandicus, a species of thermophilic archaea
isolated from hot springs in North America, Russia and
Iceland, were found to cluster genetically according to
where they were isolated [46] (the strains were all
99.8% identical based on 16S sequencing; the geographical
grouping was based on sequence divergence at nine chromosomal loci). This type of evidence has led to discussion of
the importance of isolation to microbial diversity and
evolution [47].
Against this backdrop, the questions linked to LDD of
microbes by desert dust are; (i) Are microbial species
geographically restricted and if so how? (ii) What are the
mechanisms that drive microbial distribution? (iii) What
are the limits of adaptation? Given that most of the clay soil
on carbonate Caribbean islands is derived from African
dust [48], is it possible to distinguish between ‘African’
microbes and ‘Caribbean’ microbes, assuming that microorganisms have been crossing the Atlantic with desert dust
for centuries?; and (iv) What genomic, molecular, or biochemical tools are best suited to distinguish these biogeographical distinctions?
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TRENDS in Ecology and Evolution
Does hybridization occur?
The movement of pollen in desert dust events [29] raises
the possibility of hybridization of downwind plant species
by non-native populations [49]. Models predict that
‘pure’ native plant displacement by genetic assimilation
can occur rapidly when selection favors the hybrid [49].
However, we are unaware of any reports of hybridization resulting from dust-associated pollens. From a biogeographical perspective, dust events that transport
pollen long-distances (e.g. from North Africa to
Scandinavia) introduce a potential for error in paleoecology studies that interpret past local vegetation based on
presence of pollen [50].
Future directions
While more work is clearly required on both Asian and
African dust systems, it would be of interest to have
microbiological and pollen data from the large Australian
dust events that impact New Zealand and the southern
Pacific. Each dust system is likely to have unique microflora owing to regional geographical influences; once standard methodologies have been defined (Box 2), it will be of
interest to compare the three systems.
The community composition and frequency of
occurrence data generated by these efforts could then be
integrated into an interdisciplinary, multiscale modeling
framework [51] to predict and quantify aerial LDD of
microbes and pollen in dust events. Finally, it would be
beneficial to have more scientists with an ecological background focusing or collaborating on what is essentially an
Earth surface process being studied mainly by geologists,
atmospheric chemists and microbiologists.
Summary
Huge dust events create an atmospheric bridge over land
and sea. Although satellite images leave no doubt that
desert dust particles have an intercontinental distribution,
we are only now beginning to address the questions relating to the dust-associated biological particles that also
make this trip (how many, how often, and even which
types). Data suggest that dust events can transport pathogens and allergens with the potential to impact the health
of downwind populations and ecosystems. The desire to
determine conclusively the source of dust-associated
microorganisms compliments efforts to characterize microbial diversity in terms of biogeographical patterns. More
work is needed to characterize the long-distance dispersal
of microbes and pollen by these large-scale desert dust
events and the consequences of this transport on distant
ecosystems.
Acknowledgement
We thank Betsy Boynton for creating the original illustration used in
Figure 2.
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