pncaz terra_carbon

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Building a baseline for the Cordillera Azul REDD project, Peru David Shoch TerraCarbon LLC 14 July 2010 REDDex conference Cancun, Quintana Roo, Mexico

Transcript of pncaz terra_carbon

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Building a baseline for the Cordillera Azul REDD project, Peru

David ShochTerraCarbon LLC

14 July 2010

REDDex conferenceCancun, Quintana Roo, Mexico

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An effort beyond the skill set of any one person or organization

TerraCarbon• David Shoch• Scott Settelmyer• Victor Barrena

(Facultad de Ciencias Forestales, Universidad Nacional Agraria La Molina)

• Marlon Ortega• Jedi Rosero

Centro de Conservación, Investigación y Manejo de Areas Naturales (CIMA)•Lucia Ruiz•Tatiana Pequeño•Roxana Otarola•Raul Tinoco•35 PNCAZ guardaparques

The Field Museum• Debby Moskovits• Elizabeth

Anderson• Mario Pariona• Alaka Wali• Christy

Magerkurth• Helen Howes

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Parque Nacional Cordillera Azul (PNCAZ)

• 1.4 million hectares spanning 7 provinces in 4 departments

• National park status established in 2001

• CIMA and Field Museum support park management since 2002

• CIMA and Government of Peru (SERNANP) signed a 20-year full management contract in 2008

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Parque Nacional Cordillera Azul (PNCAZ)

• For >30 years, San Martin and Loreto departments have had the highest deforestation rates in the Peruvian Amazon

• Classic agricultural frontier readily apparent from satellite imagery

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Projecting baseline rates of deforestation:

Historic trends and

Modeling from drivers

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Baseline rate of deforestation

• Modeled on basis of historic trends and driver (population)

• Reference region = PNCAZ and surrounding districts (3.8 million ha)

• Fairly uniform ecological and geographic features and demographic and socioeconomic pressures

• Timeframe: 1989 to 2003 (in the absence of conservation/ protection activities)

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Districts with < 50% forest cover in 1999 = “settled”

• Longer history of occupation with more urbanized population less directly dependent on land-use

• No strong correlation between population and deforested area

Districts with > 50% forest cover in 1999 = “frontier”

• Mostly districts directly bordering the park, represent earlier stage of colonization along the frontier gradient

• As expected, strong correlation between population and deforested area

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Projecting historic rates forward in settled districts

• Rates assessed from a time series of classified Landsat imagery (CIMA and CI): 1989 -1999 - 2003

• Net deforestation assumed to be equal to gross conservative (net deforestation always < gross)

• “Negative” deforestation (i.e. net increase forest cover) set to zero – gross deforestation can never be negative

• 10-year projection of average historic rate 1989-2003 conservative (average rate increased from 1989-1999 to 1999-2003)

• Applied as a nominal value (not %) – realistic where agricultural frontier is unconstrained (i.e. approaching an unprotected wilderness area)

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Projecting rates of deforestation in frontier districts based on correlation between population and forest area

Lugo, Schmidt and Brown 1981

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Correlating population and non-forest cover

• Data sources: – Time series of classified Landsat imagery to

produce district level forest : non-forest cover for 1989, 1999 and 2003

– Official GoP district level population data from Instituto Nacional de Estadística e Informática (INEI) for 1989, 1999 and 2003

– Official GoP district level population projections from INEI 2008-2017 (projected forward from 2007 census)

• Units: – Hectares non-forest in district– Population (total individuals) in district

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Methods and results

• Data combined for all years (n=37)• Significant correlation:

deforested area = 593 + 4.4 * population size• For each year analyzed independently, model

parameters similar and all significant (and slopes did not differ significantly among years, even though pop ↑41% and non-forest area ↑13% over the period) significance of relationship not a product of

autocorrelation Indicates relationship is stable over time and

appropriate for projections

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Projecting rates of deforestation in frontier districts based on correlation between population and forest area

• Apply relationship as a predictor 4.4 ha deforested per additional person

• Not important that the relationship be directly causal

• Assume districts with ↓ pop have zero gross deforestation conservative because deforestation continued in these districts between 1989 and 2003

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Area deforested used as the dependent variable in the model, rather than area deforested per year (i.e. annual rate)Advantages• Improved resolution – as compared with annual

rate estimates, errors around area deforested estimates (i.e. cumulative of rates) were low compared with the absolute values of the area deforested estimates

• Area deforested is more conservative than area deforested per year, because the former incorporates any reversion back to forest, i.e. is a better reflection of long-term loss of forest cover

Disadvantages• No explicit time element• Application in baseline employs simplistic

assumptions that deforestation occurs simultaneously with population increase

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Baseline projections of deforestation – overall results

• Projections to be revised every < 10 years to account for changes in land-use and population dynamics

• Resulting deforestation projected annually equivalent to 0.3 to 0.9% deforestation from 2008 to 2017 (Peru national average 0.1% annual deforestation 1990-2005; FAO Global Forest Resources Assessment)

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Thank you!

David Shoch

[email protected]

About TerraCarbon

• TerraCarbon LLC was established in 2006 as a carbon markets advisory firm specialized in the agriculture, forestry, and other land use (AFOLU) sector.

• Our mission: To provide technical and business expertise to develop high quality forest and land-based carbon projects that mitigate climate change.www.terracarbon.com.