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The increase in long distance
transport of commercial goods has greatly accelerated the previously
minor geographical dispersion of organisms. The extent to which an
organism can invade a new environment may be limited by the difficulty
of the local conditions or the complexity of the local ecosystem.
The likelihood of invasion may increase if the new ecosystem is undergoing
change, either by directly improving conditions for the guest organism
or worsening conditions for preexisting species. Nevertheless, every
ecosystem has its peculiarities. For the GRACCIE project, we are
interested in tackling two issues related to the aforementioned phenomena,
for which our local surroundings are particularly amenable. The first
is the atmospheric dispersion of microorganisms, and the second is
the entry of invader marine species into the western Mediterranean.
The microbial component of atmospheric aerosols was discovered in
the 19th century, however it has only been in the past decade that
it has gathered significant attention (Hanna, 2001). Recent studies
indicate that fungi, bacteria and perhaps viruses can survive journeys
of thousands of km in the high atmosphere, suspended in dust particles
from African desserts and propelled by the wind (Griffin et al. 2002).
The interaction between local/regional pollutants and dust has been
reported as a major reaction pathways to increase the levels of aerosols
and to change the atmospheric behaviour (nucleation of clouds and
chemistry of deposition) of the original dust emissions (Levin et
al., 1994; Alastuey et al., 2004).The magnitude of this phenomenon
and its consequences for ecosystems and humans remains poorly understood.
There have been reports of plagues and sicknesses in flora and fauna
of aquatic ecosystems in the USA that have failed to adapt to colonizing
microbes (Kellogg and Griffin 2003). Analogous events in Europe have
yet to be studied. Atmospheric aerosols also include pollen and spores
that have a large impact on human respiratory allergies. In this
context, the Iberian Peninsula serves as an ideal laboratory for
researching the atmospheric transport of biological aerosols and
Saharan dust, and for evaluating potential relationships of these
phenomena to climate change.
Introduction of new species into the ecosystems is most likely the
second leading cause of loss of planetary biodiversity; the first
being the destruction of natural habitats (Kaiser and Gallagher,
1997). Marine environments are equally susceptible to this phenomenon,
especially in costal regions, where humans have the greatest impact
(Carlton and Geller, 1993). The Mediterranean is particularly vulnerable
to fouling species; it was the cradle of many ancient civilizations,
it has a densely populated littoral, it is linked by an artificial
canal (the Suez) to a completely unrelated sea, and is a heavy transit
zone. The total number of algae species introduced into the Mediterranean
has doubled every twenty years since the beginning of the 20th century
(Ribera and Boudouresque, 1995), meaning that of the ca. 80 foreign
algae species that will arise in the next twenty years, five to ten
will be invaders (Boudouresque and Verlaque, 2002). The introduction
of invader macroalgae into Spanish coastal zones of the Mediterranean
follows similar trends and is most worrisome for the Balearic archipelago.
During the last ten years, numerous invader species have arisen in
the area: Caulerpa taxifolia (1993), Acrothamnion preissii (1994), Asparagopsis
taxiformis (1996), Womersleyella setacea (1997), Lophocladia
lallemandii (1998) and Caulerpa racemosa (1999). The
GRACCIE project aims to elucidate why have invader species have made
such a dramatic entrance in the past ten years. We believe that transport
is not the sole cause; there exists some connection to climate and
environmental changes. Possible clues may be found by studying the
similarities of the imputed species. In addition, we hope to determine
whether the dynamics of the aforementioned occupations can lead to
radical changes in littoral benthonic communities.
Alastuey A., Querol X., Castillo
S., Ávila A., Cuevas E., Estarellas C., Torres C., Exposito
F., García O., Diaz J.P., Dingenen R.V. and Putaud J.P.
(2005). Characterisation of TSP and PM2.5 at Izaña and
Sta. Cruz de Tenerife (Canary Islands, Spain) during a Saharan
Dust Episode. Atmospheric Environment, 39, 4715-4728. |
Boudouresque, C.F. and M. Verlaque (2002). Biological
pollution in the Mediterranean Sea: invasive versus introduced macrophytes. Mar.
Poll. Bull. 44: 32-38. |
Carlton, J.T. and J.B. Geller (1993) Ecological
roulette: the global transport of non-indigenous marine organisms. Science 261:
78-82. |
Griffin DW, Kellogg, C. A. V. H. Garrison, and
E. A . Shinn (2002) The global transport of dust. American Scientist. Vol
90 p. 230-237. |
Hanna H. (2001) The secret life of dust, John
Wiley and Sons, 240 pages. |
Kaiser, J. and R. Gallagher (1997) How humans
and nature influence ecosystems. Science 277: 1204-1205. |
Kellogg CA and DW Griffin (2003) African dust
carries microbes across the ocean: are they affecting human and ecosystem
health? USGS Reports 03-028. |
Levin, Z., E. Ganor, and V. Gladstein (1996). The effects
of desert particles coated with sulphate on rain formation
in the Eastern Mediterranean. J. Appl. Meteor., 35, 1511-1523. |
Ribera, M.A. and C.F. Boudouresque (1995)
Introduced marine plants, with special reference to macroalgae:
mechanisms and impact. Progress in Phycological Research 11:
188-269. |
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