Dr. Tim Baker - Human impact & global change
The macroecology of Amazonian forests: understanding current and future
trends in a changing ecosystem
Amazonian forests contain approximately 40
% of the biomass stored in terrestrial ecosystems and more than half of
global biodiversity. Predicting the effects of global environmental change
on these forests requires an understanding of the ecological mechanisms
that determine current patterns of forest composition, structure and dynamics.
For example, is resource availability, or disturbance, more important
for determining variation in forest turnover and growth rates? What role
does species composition have in determining ecosystem properties? These
questions have been addressed using long term data from a network of forest
inventory plots across Amazonia. These plots show that there are regional
scale spatial patterns in species and functional composition, aboveground
biomass, wood productivity, tree mortality and recruitment rates, and
the stocks and decomposition rates of coarse woody debris. Edaphic, rather
than climatic, conditions correlate with higher rates of forest turnover
and growth rates in western Amazonia, and compositional patterns determine
variation in forest biomass.
These spatial patterns are important because
they have provided the context for concerted increases in tree mortality,
recruitment and growth rates, and forest biomass. Overall, these trends
indicate that Amazonian forests have increased in productivity and carbon
storage and are most plausibly explained by increasing resource levels.
The known spatial variation in forest productivity, structure and composition
therefore provides a range of predictions about the future of intact Amazonian
forests. In particular, increases in the abundance of species with low
wood density as a result of elevated rates of tree turnover, may reverse
currently observed increases in forest biomass. The ecological processes
and changes in intact forests need to be considered alongside more direct
alteration of tropical forests from logging, land use and climatic changes,
to determine effective conservation strategies and the future contribution
of these biomes to the global carbon cycle.
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Prof. Paulo S. Oliveira
- Organism interactions
Dual seed dispersal systems: Interactions between ants and fleshy diaspores
in the tropics
In tropical forests nearly 90% of the shrubs
and trees bear fleshy fruits and rely on vertebrate frugivores for seed
dispersal. Thus most studies on seed dispersal of tropical species have
hitherto focused on fruit consumption and seed deposition patterns generated
by primary, vertebrate seed dispersers. However, large amounts of the
fruit crop produced by tropical trees can reach the forest floor intact,
spontaneously or dropped by vertebrate frugivores. Because tropical ground-dwelling
ants are remarkably abundant and diverse, a wide range of interactions
between ants and fallen fleshy diaspores is expected to occur in tropical
habitats. These ant-diaspore interactions can affect seed biology (germination),
modify seed fate, and markedly affect patterns of recruitment (distribution
and survival of seedlings) in primarily vertebrate-dispersed species lacking
adaptations for ant-dispersal. Such an influence of secondary dispersers
enhances the complex, two-phase nature of the dispersal ecology of tropical
tree species. Untangling the complexity of such dispersal systems (with
sequentially-connected phases) is crucial for understanding the evolutionary
relationship between frugivores and plants, and plant regeneration pathways.
Mutualisms are less conspicuous in dispersal systems than in more tightly
coevolved systems, and interactions between ants and fleshy diaspores
are highly unpredictable and variable. Indeed, the intricacy of the mutualistic
networks within such dispersal systems may underlie the biotic complexity
and high diversity of tropical ecosystems.
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Prof. Robbert Gradstein - Biodiversity
Bryophyte assemblages of tropical rain forests - responses to forest modification
and global warming
Tropical rain forests because of their structural
complexity and favorable microclimatic conditions are a rich habitat for
bryophytes. Owing to the lack of a protective cuticle, solutions and gases
may enter freely into the living tissues of these plants causing sensitive
reactions of these plants to changes in the environment. Because of this,
bryophytes are good ecological indicators. Based on results of our work
in tropical America and Asia I will discuss spatial patterns of bryophyte
diversity in different rain forest types, responses to forest modification,
and the possible impact of global warming on bryophyte diversity. Evidence
from bryophytes allows for recognition of new, hitherto overlooked type
of rainforest: the Tropical Lowland Cloud Forest (TLCF) with record-high
diversity. Analysis of bryophyte assemblages along disturbance gradients
shows that old-growth primary forests are not necessarily more diverse
than secondary ones. Diversity in plantations and on remnant trees, however,
is significantly reduced. Canopy closure is an important parameter influencing
bryophyte diversity along the disturbance gradient. Similarity in species
composition of secondary and primary forests increases with forest age
but after 40 years of succession many primary forest species had not re-established
in secondary forest, indicating that long time is needed for recovery
of bryophyte communities. The possible impact of global warming on tropical
bryophyte diversity was studied by translocation of bryophyte assemblages
along temperature gradients in the Andes. The results show species-specific
responses to transplantation after two years and indicate that community
structure and species composition of bryophytes in tropical rain forests
may be significantly modified as a result of future temperature increases
of two or more degrees.
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Prof. Timm Hoffman - Biodiversity
Global change and human impacts on biodiversity in Namaqualand, South
Africa
TIMM HOFFMAN, Institute for Plant Conservation,
Botany Department, University of Cape Town, Private Bag X3, Rondebosch,
7701, South Africa. Tel: +27-21-650-2440. thoffman@botzoo.uct.ac.za
RICK ROHDE, Centre for African Studies, Edinburgh
University, Edinburgh. Tel: +27-21-461-5921. rick.rohde@ed.ac.uk
Two perceived threats face the biota of Namaqualand.
Firstly, recent modelling efforts suggest that climate change will impact
heavily on the diversity and agricultural production of the region as
a result of a reduction in rainfall and an increase in temperature over
the next 50 years. Secondly, the expansion of communal land under South
Africa's land reform programme could lead to higher stocking rates over
a significant portion of Namaqualand on a scale not seen in the region
since the 1950s. This trend could be exacerbated as a result of the downscaling
of mining operations in the region and the retrenchment of workers who
use their severance packages to invest in livestock production. To investigate
these issues we take an historical perspective. We look at historical
trends in rainfall over the last 100 years and incorporate recent interpolation
studies carried out by colleagues within the BIOTA South research programme.
Evidence for the impact of climate change is investigated for two long-lived
tree Aloe species growing in the broader Namaqualand region. The apparently
contradictory results suggest that responses to drought and high rainfall
events are complex and the life history dynamics of long-lived species
need to be better understood. The historical impact of human society in
the region from pre-colonial to recent times is also outlined. Changes
in the area cultivated and stocking rate for communal and private land
suggests that the last two decades has seen a significant decline in the
agricultural use of the land. While the low-lying bottom lands continue
to be the most heavily exploited, increased urbanisation in the region
has drawn a large number of people off the land, particularly in the last
few decades. Improved infrastructural development in the rural areas of
Namaqualand has also meant that people are now less reliant on natural
resources for their day-to-day activities. Firewood production in a recently-electrified
rural village, for example, has seen a 75% reduction in fuelwood consumption.
The strong environmental history and repeat photography approach undertaken
in this analysis suggests that Namaqualand's landscapes are similar to
what they have looked like in the last 100 years. If anything, there is
more vegetation cover today than there was 50 years ago and there is little
evidence of widespread desertification in the region. Land use impacts
were probably greatest in the first half of the 20th century and have
declined in the last 50 years.
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Prof. Teja Tscharntke - Human impact & conservation
Plant-insect diversity and ecosystem functioning in human-dominated tropical
landscapes
The modification of tropical landscapes through
human exploitation of the environment continues to reduce biodiversity
on a global scale. This decline in biodiversity has led to concern over
the potential loss of major ecosystem processes. Further, agricultural
land use and biodiversity conservation have been traditionally viewed
as incompatible, but only recently, recognition has increased that a restriction
of conservation efforts to natural, undisturbed ecosystems is of limited
value. Agriculture can make important contributions to high diversity
of landscapes, while it also benefits from sustainable ecosystem services
provided by agricultural conservation management at local and regional
scales. For example, enhanced biological pest control and improved crop
pollination may directly increase the farmers' income.
In this presentation, I will refer to results
on patterns of biodiversity and plant-insect interactions, changing with
spatial and temporal scales considered, from the Collaborative Research
Centre "Stability of Rainforest Margins in Indonesia" (STORMA, SFB 552)
and the BioTEAM (BMBF) research program on the "Evaluation of biological
diversity of land-use systems in a mega-diverse region of Ecuador" (Bio-Sys).
References:
Klein, A, Steffan-Dewenter, I., Tscharntke,
T. (2003): Fruit set of highland coffee increases with the diversity of
pollinating bees. Proceedings of the Royal Society of London, Series B
270: 955-961.
Olschewski, R., Tscharntke, T., Benítez, P.
C., Schwarze, S., Klein, A. M. (2006): Economic valuation of pollination
services and pest management comparing coffee landscapes in Ecuador and
Indonesia. Ecology and Society.
Tscharntke T., Klein, A.M., Kruess, A., Steffan-Dewenter,
I., Thies, C. (2005): Landscape perspectives on agricultural intensification
and biodiversity-ecosystem service management. Ecology Letters 8: 857-874.
Tylianakis, J., Klein, A.-M. , Tscharntke,
T. (2006): Spatiotemporal variation in the diversity of Hymenoptera across
a tropical habitat gradient. Ecology (in press).
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