Similar a Cristina BRANQUINHO "Searching for universal early-warning indicators of desertification: anticipating tipping points at ecosystem level" (20)
Cristina BRANQUINHO "Searching for universal early-warning indicators of desertification: anticipating tipping points at ecosystem level"
1. “Searching for universal early-warning
indicators of desertification: anticipating
tipping points at ecosystem level ”
Cristina Branquinho1, Pedro Pinho1,2, Alice Nunes1,3,
Paula Matos1,3, Melanie Batista1, Adriana Silva1,
Andreia Ferreira1 and Lúcio do Rosário4
1Universidade de Lisboa;
2Universidade Técnica de Lisboa;
3Universidade de Aveiro; Ciência 2007
4Instituto de Conservação da Natureza e Florestas; LTER/BIA-BEC/0048/2009
PTDC/AAC-CLI/104913/2008
2. Drylands
• Cover about 41% of Earth’s land surface supporting over 38% of the global
human population
• Semi-arid areas are the most vulnerable to DLD
Millennium Ecosystem Assessment (2005) Ecosystems and Human Well-Being: Desertification Synthesis (World Resources
Institute, Washington, DC).
4. Mechanisms of transitions between ecosystems states and tipping points
An ecosystem experiences a shift to a new state, with significant changes to
biodiversity and the services to people it underpins, at a regional or global scale.
Tipping points also have at
least 1 of the following
characteristics:
✤ The change becomes self
perpetuating (deforestation
reduces regional rainfall,
which increases fire-risk,
which causes forest dieback
and further drying).
✤ There is a threshold beyond
which an abrupt shift of
ecological states occurs.
✤ The changes are long-
early warning lasting and hard to reverse.
✤ There is a significant time
lag between the pressures
and the appearance of
impacts.
Secretariat of the Convention on Biological Diversity (2010) Global Biodiversity Outlook 3.
5. Ecosystem functioning is extremely complex and thus monitoring the effects of
environmental change factors in ecosystems in an integrative perspective can
make use of ecological indicators.
6. Hypothesis/Assumptions
• It is possible to find early warning indicators of
tipping points.
• Those indicators are most probably ecological
indicators which reflect in overall an integrated
response of the ecosystem.
• Indicators based on biodiversity changes can be
one of those indicators.
• Without time we can use gradients in space to
give us a clue about possible good indicators.
7. Does all species have the same value?
Ecosystem Processes
Biodiversity
M. Scherer-Lorenzen, (2005), BIODIVERSITY AND ECOSYSTEM FUNCTIONING: BASIC PRINCIPLES, in Biodiversity: Structure and Function, [Eds. Wilhelm
Barthlott, K. Eduard Linsenmair, and Stefan Porembski], in Encyclopedia of Life Support Systems (EOLSS),, Oxford ,UK
8. Functional Diversity – Potentially Universal
Functional diversity: groups according to common response to the
environment and/or common effects on ecosystem processes/functions
• Has been shown to relate
with several environmental
constraints (e.g. nutrient
availability, grazing, fire,
etc.)
•
• Independent from local
communities composition -
potential to be universal
Díaz, S. & Cabido, M. (2001) Trends in Ecology & Evolution 16, 646-655.
Lavorel, S. et al. (2007) Plant Functional Types: Are We Getting Any Closer to the Holy Grail? Springer-Verlag, Berlin Heidelberg. pp.
149-160.
9. Study site
Portugal susceptibility to DLD
Aridity Index
sub-humid and humid
dry sub-humid
semi-arid
Mediterranean climate with Montado, an agro-pastoral system dominated by
holm-oak (Quercus ilex L.) woodlands
Study transition in a spatial aridity gradient
Source: Autoridade Florestal Nacional
10. Selection of the DLD gradient
Homogeneous conditions
Stratified sampling (precipitation,
(Holm-oak open woodlands, grazing
temperature, aridity indices, etc.)
intensity, lithology, slope, fire
occurence, etc.)
precipitation soil organic C
Aridity Evapotransp.
Susceptibility Temperature
a
Random selection of sites (≥60)
11. establishing relation between climate and biological variables
1) Lanscape scale – remote
sensing analysis
2) Using plant Functional
diversity
3) Using lichen Functional
diversity
desertification and land-degradation gradient
14. 2) Using Plant functional diversity
Legum. Non legum.
• Point-line intercept transect method
• A priori functional groups (e.g. life cycle, life form, etc.) and measured traits (e.g.
SLW, height, etc.)
16. 2) Using Plant functional diversity 24 sites analyzed
Plant functional shifts
80
Functional groups cover
60 Annual
graminoids +
Plantago sp.
(%)
40
Perennial
graminoids +
20
Annual N-
fixing
0
500 550 600 650
Last 50 Years average precipitation (mm)
17. 2) Using Plant functional traits 14 sites analyzed
40
SLA T. barbata (m2kg-1)
30
20
10
0 Measured only for 2 species
500 525 550 575 600 625 650
Last 50 yr precipitation (mm)
25
Veg. height V. myurus (Q90)
20
15
10
5
0
0.4 0.5 0.6 0.7 0.8
Aridity index
Measured for all species
18. 3) Using lichen Functional diversity
Standard
“European
method”
L DV (lichen
diversity value)
Asta, J., et al, 2002. Monitoring with Lichens, Kluwer Academic Publisher.
19. 3) Using lichen Functional diversity
lichens functional diversity as early warning of
desertification
Hygrophytes
Xerophytes
annual average
precipitation (mm)
20. 3) Using lichen Functional diversity
Does lichen diversity respond to climate over time?
Before: 2002 After: 2003
21. nal Remarks
Functional diversity (plants and Lichens) seems to be a
good candidate for early warning since it respond to
changes in climate and desertification gradients.
Moreover has the potential to be universal.
We are contributing to the 3 UN "sister Conventions":
on biodiversity-CBD, climate change-UNFCCC and
desertification-CDD, that relay in ecological indicators of
biodiversity and ecosystem goods and services
evaluation.
We are willing to test this hypothesis in other countries.
Thank You!
Notas del editor
the risk of land degradation is greatest in the median section of the aridity gradient (mostly the semiarid drylands), where both sensitivity to degradation and population pressure (expressed by population density) are of intermediate values.Para avaliar a eficácia da convenção na área da sustentabilidade, da gestão dos solos e da gestão dos ecossistemas;UN criou um processo de monitorização e avaliação;Adoptou 11 indicadores de impacte em 11 países entre os quais PT
Theoretically, rates of ecosystem processes might increase linearly with species richness if all species contribute substantially and in unique ways to a given process — that is, have complementary niches. However, when different species have similar functions at the ecosystem level this relationship is likely to saturate as niche overlap and ‘redundancy’ increases at higher levels of diversity. enabling to evaluate vegetation response both in the form of species turnover, shifts in abundance and/or morpho-functional traits
These traits relate to resource acquisition and retention, decomposition and stress avoidance/tolerance