Marion and Prince Edward Islands are situated in the
sub-Antarctic region about 2100 km southeast of Cape Town. Their
climate is cold and wet; annual mean temperature is 5.6°C and mean
annual precipitation (mainly rain rather than snow) is 2326 mm per
year. The high precipitation is associated with much cloudiness so
that on average there is less than 4 hours of sunshine per day.
Winds are fierce and gales occur on about 100 days per year.
However, the islands’ climate is changing. Annual mean air
temperature on Marion Island has increased by 0.04°C per year since
1969. Annual precipitation at Marion Island has decreased since the
mid 1960s, so that the 1990s was the driest of the five decades that
precipitation has been measured at the island. The annual total
sunshine hours showed an average increase of 3.3 hours per year
between 1951 and 2002.
Hence, Marion Island (and almost certainly also Prince Edward
Island, which is only 22 km away but for which there is no climate
data) is becoming warmer, drier, and sunnier. These climatic changes
have implications for the islands’ plants and animals, which have
evolved under the cool, humid conditions typical of sub-Antarctic
islands. To understand these implications it is necessary to realize
that there are differences in the way ecosystems develop on oceanic
islands compared with on continents. At the heart of this difference
is that continental ecosystems have a large pool of species to draw
on, whereas oceanic islands are remote, initially have no species on
them, and their ecosystems depend on whatever plants, animals, and
microbes can reach them by long-distance dispersal. Marion and
Prince Edward Islands, for instance, originated as undersea
volcanoes only about a half-million years ago, long after Africa
split off from Antarctica and migrated north to its current
position. The islands were thus never connected to, or even near,
any continent. The pool of plant and animal species on the islands
is made up a relatively few species that managed to somehow reach
the islands over long distances across the ocean. Many important
functional groups of plants and animals are not adapted to such
long-distance dispersal and so do not occur on the islands naturally
(i.e., they are not indigenous to the islands). By functional group
is meant a group of species that "do the same sort of
thing" ecologically. Examples of such groups that do not occur
on Marion or Prince Edward Island are terrestrial mammalian
herbivores and carnivores such as the cud-chewing buck and deer and
the predatory cats and dogs that are so characteristic of the
ecology of continents, especially Africa. Less conspicuous (but
ecologically extremely important) animals are also absent; for
example there are no frogs, reptiles, rodents, or rabbits. Even the
insect fauna of the islands is species-poor, although in some
habitats the few insect species that do occur may be present in high
numbers. Overall, then, like all oceanic islands, biodiversity
(species-richness) at Marion and Prince Edward Islands is low.
This low biodiversity, especially the absence of important
functional groups such as herbivores and carnivores, affects
ecological functioning at the islands. Ecological functioning has to
do with the flow of energy and the cycling of nutrients in the
ecosystem. Energy reaches the island as sunlight, which is fixed by
plants and results in their growth. The amount of vegetation growth
over a year is termed the annual primary production. Since there is
no dry season and no really bitterly cold weather to stop plant
growth, annual primary production is high on the island. The
vegetation needs to take up a substantial amount of nutrients to
support that growth. Climatic warming might be expected to increase
productivity and the demand for nutrients even further. But will it?
In most ecosystems, herbivores eat the produced plant material and
excrete a portion of the nutrients—they thus play an important
role in recycling nutrients, making them available for re-use by the
plants. Without herbivores (even the insects feed mainly on plant
litter and microorganisms) the nutrients taken up by the growing
plants remain trapped in the plant material, which dies to form
plant litter. Decomposition of the litter releases the nutrients in
a form that can be taken up by plants again. Hence, nutrient
recycling on the island occurs mainly through decomposition, rather
than grazing. However, decomposition (and hence nutrient release)
occurs only slowly in the cold, wet island soils, unless assisted in
some way. Insects (especially the larvae of moths, weevils, and
flies), snails, and earthworms provide that assistance, by feeding
on plant litter. The litter is partly broken down in the animal’s
gut and egested in a form that is easier for soil microorganisms
such as bacteria and fungi to break down further. Insects and
earthworms thus play an important role in the processes of
decomposition and nutrient cycling; in fact, it has been estimated
that they make available up to 88% of the nutrients required by some
vegetation types on the island.
Since the insects and earthworms are cold-blooded, their activity
is strongly temperature-dependent. Increasing temperature, as is
happening at the islands, should thus result in enhanced rates of
litter consumption and hence of nutrient release, which will allow
the potential for increased primary production due to elevated
temperature to be realized. But will this happen?
House mice (Mus musculus, the same species that can be
caught in most houses the world over) occur on Marion Island, having
been introduced there by sealers. The mice feed mainly on adults and
larvae of moths, weevils, and flies, and on earthworms and snails,
the very same invertebrates that are so important in driving
ecosystem functioning on the island. It is estimated that that mice
annually consume between 1 and 6 times the average population size
of their invertebrate prey species. Such high consumption rates have
a particularly severe effect on the island’s invertebrates, as is
clear from comparisons of the invertebrate populations of Marion
Island with nearby Prince Edward Island, where mice do not occur.
There are big differences in the size, structure, and composition of
the insect populations of the two islands, and also in the maximum
body size attained by the various species. Mice are even preventing
speciation of weevils on Marion Island by feeding preferentially on
adult weevils of a specific size.
This predation by mice on soil invertebrates is also affecting
other components of the Marion Island biota. For example, the
lesser sheathbill (Chionis minor) is the only non-migratory
bird species on the island and relies on soil macroinvertebrates as
food in winter. Between the mid-1970s and mid-1990s the sheathbill
population on Marion Island decreased by 23% whereas the one on
Prince Edward Island did not change. Another example is the sedge, Uncinia
compacta, which rarely manages to set seed on Marion Island
since mice remove the seed long before it ripens. As a result, the
sedge is a much more important component of the vegetation on Prince
Edward Island than it is on Marion Island.
More insidious, but probably even more profound than these direct
effects of house mice on the island's biota, is their
influence on ecosystem function through their removal of the
cardinal agents of energy flow and nutrient cycling at the island.
For instance, it is estimated that predation by mice on moth larvae
alone prevents the consumption of 1000 kg plant litter per hectare
per year, a decrease of about 40% compared with what would be
consumed in the absence of mice. There is evidence that the island’s
mouse population has increased since it was first studied in
1979/80, possibly due to climatic warming and/or the fact that the
island’s feral population of domestic cats was eradicated in the
early 1990s. An increasing mouse population translates into greater
predation pressure on the invertebrates and hence in lower rates of
nutrient cycling. This will result in less nutrients being available
to the plants which will result in a lower primary production and,
more importantly, the plant material that is produced will have a
low nutrient quality. This will lead to low-quality litter which
decomposes even more slowly. The net result will be that peat will
accumulate faster than it does at present. Peat accumulation is a
major driving force for ecological succession on the island. By
"ecological succession" is meant the process by which one
type of plant community replaces another. Most of the habitats on
the islands are very wet—the water table is close to or even at
the surface, as in bogs and mires. As peat accumulates it raises the
whole community above the watertable and allows the development of a
drier type of community.
House mice are only one example, albeit a striking one, of the
far-reaching effects that an introduced organism can have on the
biology and ecology of Marion Island. Climatic warming can be
expected to increase the ease with which the island can be invaded
by alien species and there is already evidence of this. The
Kerguelen cabbage (Pringlea antiscorbutica) is found only on
four sub-Antarctic island groups, including the Prince Edward
Islands. The species is one of the last—and perhaps the only—remaining
relic of a once extensive circum-Antarctic flora and has a special
place in sub-Antarctic folklore since it was used by sailors,
sealers, and whalers to prevent scurvy. On Marion Island its
distribution and abundance has declined alarmingly over the past 20
years for several reasons, all to do with invasive alien biota.
The European slug (Deroceras caruanae) was introduced to the
island in the mid 1960s and increased in abundance and distribution
in the 1990s. The Kerguelen cabbage is one of its preferred food
items there. The Diamondback cabbage moth (Plutella xylostella L,),
a major pest of crucifers (cabbages, cauliflower, brussel sprouts),
is a recent arrival on the island (first discovered in 1986). It
severely affects P. antiscorbutica, which is its only host
plant there. Botryotinia fuckeliana, the fungus that causes
grey mould rot in crucifers and other vegetable crops, has also
reached the island through vegetables sent as food for the island
personnel (a practice that has been discontinued). Many stands of
the cabbage have been infected by the fungus, whole plants
collapsing into a black slimy residue.
The study of oceanic islands has been cardinal in developing and
testing key aspects of biological and ecological theory, such as
evolution, speciation, biogeography, and ecosystem dynamics. The
account given above suggests that sub-Antarctic islands have
particularly much to offer in furthering our understanding of a
topical and important theme in biology worldwide—how organisms and
ecosystems respond to climatic change. Global warming is especially
intense in the sub-Antarctic region and because of their isolation,
species-poor biota, and harsh environments; sub-Antarctic
island ecosystems are relatively simple and sensitive to
perturbations. They are therefore ideal "ecological
laboratories" for studying how organisms, ecological processes,
and whole ecosystems respond to a changing climate.
Professor Valdon R. Smith
Department of Botany and Zoology
University of Stellenbosch
Matieland, South Africa