The Future of the Tropical Forests of Amazonia
Carlos A. Nobre Ministry of Science, Technology and Innovation of Brazil
UNESCO Paris, 9 December 2014.
The Amazon in the ‘Anthropocene’: The 'Great Amazonian’ Acceleration Total Population [#]
Urban Population [#]
30000000
Cities & Towns [#] 1000 800 600 400 200 0
20000000 15000000
20000000
10000000 10000000
5000000 0
0 1900
1940
1960
1980
1900
2000
1940
1960
1980
2000
1900
1950
1970
1990
2010
Indigenous /Conservation Areas [#]
Roads [km] 80000
1000
60000
800
40000
600
20000
400
0 1900
1950
1970
1990
200
2010
0 1900
200 000 000
200000
400000 150 000 000
150000
0 2010
Cumulative Deforestation [km2]
100000 0
1900 1950 1970 1990 2010
0 1990
2010
200000
50 000 000
50000
1970
1990
300000
100 000 000
100000
1950
1970
Cattle herd [#]
Unofficial Roads [km]
1900
1950
1920
1950
1970
1980
1995
Brondizio 2013
Risks to the Natural Systems in Amazonia
Does the 'great acceleration ’ globally and regionally pose a risk to the ecosystems of Amazonia?
Forestsp rovide important economic and ecological services …
5
Amazonian Ecosystems Service • Maintenance of global carbon cycle (15% of global N for anthropogenic CO2)
• • • •
Powerful hydrology (20% of fresh water flow into the glob Biodiversity richness (> 10% of species) Climate stabilization (key heat source for the atmosphere) Helps to maintain cultural and etnic diversity (ove populations, language diversity)
04.Feb.2013 06:00 UTC
© Celestia
6
Amazon: a sink of about 0.5 ton C/ha/year over 350 MtonC/year
Amazon Biomass is increasing over time (green arrows) Is this a CO2 “fertilization” effect? Phillips et al. 2009 Science
But, the reality of agricultural expansion in the Amazon is one of fire and forest destruction …
Ecosystems of Amazonia ‐ environmental drivers of change Complex Earth System Models are needed to study all these interacting and simultaneous drivers
Land Cover Change Climate Change
Fire
Climate Extremes
Anthropogenic and Natural Drivers of Environmental Change in Amazonia
Warming of 0.8°C in Amazonia (Victoria et al., GLOBAL WARMING 2004. J Climate); 3°‐4°C by 2100 (IPCC AR5, 2013)!
Can global warming have a discernible effect in the Amazon?
Consequences of Climate Change on the Biome distribution in Tropical South America
Model Projections: Tropical rainforest will be replaced by savannah! 18% to 48% by the end of the 21st Century Projected distribution of natural biomes in South America for 2090‐2099 from 15 AOGCMs for the A2 emissions scenarios, calculated by using CPTEC‐INPE PVM. Salazar, Nobre et al., 2007 GRL
What is going on right now in terms of climate variability and change in the Amazon?
Record‐breaking droughts (2005, 2010) and floods (2009, 2012, 2014)
2005
2012
Rio Manaquiri, a 150 km de Manaus
2010
2014
Is this an expected manifestation of natural climate variability?
Or could it be an early sign of climate change due to global warming?
What is going on right now in terms of climate variability and change in the Amazon?
Record‐breaking droughts (2005, 2010) and floods (2009, 2012, 2014)
2005
2012
Changes in extreme flow in Amazon Rio Manaquiri, a 150 km de Manaus River (medium confidence, major contribution from climate change) (IPCC/ WGIIAR5, 2014)
2010
2014
Warming of 0.8°C in Amazonia (Victoria et al., 2004. J Climate); 3°‐4°C by 2100 (IPCC AR5, 2013)!
GLOBAL WARMING
Total deforested area (clear‐cutting) is 765,000 km2 in Brazilian Amazonia (20%) (INPE, 2014)
DEFORESTATION
Anthropogenic and Natural Drivers of Environmental Change in Amazonia DROUGHTS
FOREST FIRES
What are the synergistic effect of global warming + deforestation + fires? Forest fire frequency ↑ (Nepstad et al., 2006)
Projected distribution of natural biomes in South America more than 2/3 of the models used ≥ 6 models) coincide for 2050 from 9 Earth System Models for the RCP 8.5 emission scenarios
Combined Effects Climate Change + Deforestation + Fire + CO2 ‘Fertilization’ (25%)
Forest
= Savannah
20% Def.+ Fire
Deforestation at 20% + Fire effect
+ Climate Change Scenario of IPCC AR5 (RCP8.5) in 2050
+ CO2 ‘Fertilization’ Effect at 25% Tropical Seasonal Forest Savannah Tropical Evergreen Forest
Source: Sampaio et al., 2014, unpublished.
Fraction of the remaining forest area for the entire Amazonia Climate change projections – CMIP5 – 9 Earth System Models (ESM) DEFOR. ONLY
RCP 2.6 RCP 4.5 RCP 8.5
CC+20% Defor.+Fire 2050
50%
40%
20%
RCP 2.6 RCP 4.5 RCP 8.5
CC ONLY 2050
2025
2050
2025
Projected reductions of over 50% of Forest cover by 2050!
2050
Source: Sampaio et al., 2014, unpublished.
Maximum speeds at which species can move across landscapes
Trees can move only a few km per decade and would be 'outraced’ by the climate change velocity (for Amazonia, at least 20 km/decade for RCP 4.5)
Based on observations and models; vertical axis on left and compared with speeds at which temperatures are projected to move across landscapes (climate velocities for temperature; vertical axis on right). IPCC AR5 WGII, 2014
‘Tipping points’ in Amazonia
Equilibrium states
Tropical forest in equilibrium with current climate: one stable equilibrium state Savanna state triggered by climate change and/or deforestation: two stable equilibrium states Stability of savanna enhanced by increased droughts and fires Environmental variation
Cardoso and Borma, 2010 Borma, Nobre and Cardoso, 2013
Quantifying ‘Tipping points’ in Amazonia Bi‐stability with two stable states: Forest and forest‐savanna
ΔT > 3.5 C Deforest. > 40%
Observations ΔT ≈ 1 C Deforestation ≈ 20% Lengthening of dry season (?)
32 years December January February March April May September October November June July August
Decreasing trends for the SON period, i.e., the end of the dry season and the beginning of the rainy season.
Dubreuil et al, Environ Monit Assess (2012) 184:877–891
REGIONAL CLIMATE PROJECTIONS: TEMPERATURE CHANGE FOR THE AMAZON
For high emission scenarios, temperature Increase exceeds 4 C in the Amazon
December‐February Temperature Change for the Amazon
June ‐August Temperature Change for the Amazon
‘Tipping points’ in Amazonia Bi‐stability with two stable states: Forest and forest‐savanna
ΔT > 3.5 C Deforest. > 40%
Even if tropical countries cut deforestation to zero, uncheked global warming will wreak havoc to the Amazon forest!
Science‐police interface for reducing deforestation Global Fossil Fuel and Land Use Change Emissions of GHG Total global emissions: 39.4 ± 3.4 GtCO2 in 2013, 42% over 1990
Fossil fuel emissions continue to go up …
% of land‐use change emissions to global emissions: 36% in 1960, 19% in 1990, 8% in 2013
Three different methods have been used to estimate land‐use change emissions, indicated here by different shades of grey Source: CDIAC; Houghton et al 2012; Giglio et al 2013; Le Quéré et al 2014; Global Carbon Budget 2014
Policies to reduce Amazon Deforestation 2008
Prevention and Control of Deforestation in the Legal Amazon (PPCDAM). Coordinated activities among government agencies; Introduction of real‐time remote‐sensing forest monitoring technology Extensive expansion of protected territories.
Targeting of priority municipalities ‐ prevention, monitoring, and combating of illegal deforestation Revision of legislation ‐ environmental infractions and respective sanctions. Conditioning of rural credit.
2004
35000 30000
2008 PRODES/INPE
25000 20000
4848
15000 10000 5000
Annual deforestation rates in Brazilian Amazon
0 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014
Deforestation rates (km2/year)
2004
Years
Source: Assunção et al. (2012)
Net profitability of current economic activities in the Amazon and versus the potential for REDD CATTLE
US$ 20 a 70 per ha/year REDD
US$ 2.000 to 2.400 per ha (at US$ 20 per ton C)
SELECTIVE LOGGING
US$ 100 to 400 per ha/25‐ to 30‐year cycle SOYA
US$ 100 to 200 per ha/year
Decoupling agricultural production and deforestation
120
Historical agricultural commodities prices in Brazilian Amazon (2004‐2013)
Deforestation is the main cause of unsustainability of agriculture
Price (R$)
100 80
Meat
60
Mato Grosso
40
Tocantins
20 o Agricultural expansion and deforestation rates: 0 both processes have long been connected in Brazil. 2004 2005 2006 2007 2008
Example: Decoupling of deforestation and soy production
1990s in the southern Amazon during the late 2000s o Peaks in cropland area and
Pará 2009
2010
2011
2012
2013
Year
cattle herd size coinciding with Source: peaks in deforestation in Amazonia and in the Cerrado region. http://www.agrolink.com.br/cotacoes/
o
2000s
Historico.aspx Annual deforestation trends began to diverge from fluctuations in cropland Obs: Adjusted prices with IPCA index using 2010 as the base year
area and cattle herd size.
o Deforestation in all Brazilian biomes plunged to the lowest rates since monitoring began. o Nevertheless, the link between agricultural expansion and deforestation has weakened rather than disappeared completely ‐ as the small resurgence in Amazonian deforestation in 2008 by increases in cropland area and cattle Macedo et al., 2012herd - PNAsize.
Ministério da Ciência, Tecnologia e Inovação Secretaria de Políticas e Programas de Pesquisa e Desenvolvimento Coordenação Geral de Mudanças Globais de Clima
Gross emissions by sector Emissions of 2,36 billion ton of CO2eq in 2005
Emissions of 1,52 billion ton of CO2eq in 2012
14% Energy Land Use and Forest
Agriculture
2% 3%
29%
32%
18% 3%
63%
6% 29% Energy
Waste Treatment
Industrial Process
Agriculture
Land use and forests
Aguiar et al., 2013
Which future do we want for the Amazon? OBSERVED Deforested Area (%) in 2010
Scenario A
Scenario B
Sustainability?
Fragmentation?
declining deforestation rates
weakening of policy of recent years
Model Projections in 2050
Modeling gives a glimpse of the potential land use change dynamics up to 2050
Payment for Environmental Services (e.g., REDD+) Conserving Forests Through Periodic Grants: “Bolsa Floresta”, Amazonas State, Brazil
How to use Amazon biodiversity sustainably and at the same time benefiting the local population? The Açaí Case Economic output of açaí to Amazonia = US$ 2.5 billion/year
Natural dye indicator for dental plaque
Net Economic Net Return of Açaí Production in the Amazon Basin Pará State : US$ 206.6 to US$ 2,272.7 ha/yr (for managed and unmanaged sites)
Jardim and Anderson (1987) Hiraoka (1994a, 1994b) Brondizio, E. (2007)
Local benefits, but value aggregation away from the region Adding value through the commodity chain 1 hectare equivalent of açaí fruit $140,000
US$/ha of fruit production
$120,000
$100,000
$80,000
$60,000
$40,000
$20,000
$0
Exhibit ‘Acai: from local to global’: Mathers Museum of World Cultures, Indiana University Brondízio, 2014.
Regional resource economies do not translate into revenue for municipalities Low HDI in açaí producing municipalities
HDI Source: NYT
Source: Google
• … the pressure on social services, climate change impact, health vulnerability, and pollution is felt up close and where concrete solutions are demanded Brondízio, 2014.
We need a new economic sustainability paradigm for the tropical forests... “ To add value to the heart of the forest”. Bertha Becker Science and technology must offer solutions for the emergence of an innovative, local bioindustry Along with empowerment and mass education of the forest people.
Merci! Thank you!
Duration of dry season (months) in the Arc of Deforestation Region. Hovmoller diagram of monthly rainfall from 1951‐2010 for southern Amazon.
75°W‐50°W, 15°S‐5°S
100 mm/month
IPCC/AR5: CMIP3 models and downscaling experiments show over southern Amazonia, northeastern Brazil and eastern Amazonia, the maximum number of consecutive dry days tends to augment, suggesting a longer dry season. Marengo et al. (2011)
Madeira River Flood, SW Amazon, 2014 2400 2200
Madeira River Water Levels at Porto Velho 2014 hydrograph Peak flows of 65,000 m3/s
2000
Water Level (cm)
1997
1800
overflow
1670 1580
1600 1426
1400 1200
Maximum (2008‐2013)
1000 800 2014 cota de transbordamento Média (2008‐2013)
cota de alerta 1997 Mínimo (2008‐2013)
Ministério da Ciência, Tecnologia e Inovação Secretaria de Políticas e Programas de Pesquisa e Desenvolvimento Coordenação Geral de Mudanças Globais de Clima
Brazilian GHG gross emissions: Period 1990-2012 in CO2eq 3000
2500
Tg CO2eq
2000
1500
Land use and forests
1000
Agriculture
500
Energy
0
1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012
Energy
Waste Treatment
Industrial Process
Tg = million ton . GWP CH4: 21; GWP N2O: 310
Agriculture
Land use and forests
REGIONAL CLIMATE PROJECTIONS: PRECIPITATION CHANGE FOR THE AMAZON
41
Global terrestrial carbon sink is dominated by Tropical Forests
~30% goes into terrestrial ecosystems
Net CO2 flux (1901‐2010, kgC/m2/y
~50% of anthropogenic CO2 remains in the atmosphere
‐1 ‐
‐2 ‐
Carbon sink is largest in the Tropics
‐3 ‐
‐4 ‐
‐80 Le Quéré et al. 2009 Nature Geoscience; Schimel et al. 2014 PNAS
‐40
0 Latitude
40
80
Science police interface for reducing deforestation Land Use Change Emissions of GHG Total global emissions: 39.4 ± 3.4 GtCO2 in 2013, 42% over 1990
Fossil fuel emissions continue to go up, but emissions from tropical land‐use change are declining.
% of land‐use change emissions to global emissions: 36% in 1960, 19% in 1990, 8% in 2013
Three different methods have been used to estimate land‐use change emissions, indicated here by different shades of grey Source: CDIAC; Houghton et al 2012; Giglio et al 2013; Le Quéré et al 2014; Global Carbon Budget 2014