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REDD+ baselines: what are the crucial ingredients?

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A presentation by Casey Ryan, from the University of Edinburgh, at a workshop held in Paris from Thursday, 3 December to Friday, 4 December during the 21st Conference of the Parties (COP21).

The event organised by the International Institute for Environment and Development aimed to share the findings of its research to inform a wider debate on how REDD+ is contributing to addressing the drivers of land use and land use change.

The presentation focused on land cover change and creating baselines.

More details: http://www.iied.org/redd-paris-what-could-be-it-for-people-forests

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REDD+ baselines: what are the crucial ingredients?

  1. 1. IIED, Paris, Dec 4th 2015 REDD+ baselines: what are the crucial ingredients? Casey Ryan, Iain McNicol, Becky Stedham, Yaqing Gou, Neha Joshi and Nick Berry Senior Lecturer, University of Edinburgh, School of GeoScience, UK In collaboration with the TREDD team, coordinated by IIED
  2. 2. The ingredients of a useful baseline 1. historical information about land cover change 2. understanding of the causes and drivers of change 3. an extrapolation into the future, taking account of potential new drivers challenge no.1: good historical information on land cover and drivers challenge no.2: “[Social] scientists are good historians. … But they have not been good forecasters” (Lipset 1983:157) Woodland cover Time 1991 2000 2007 2027? Project A B Baseline C
  3. 3. Historical land cover information ❖ ingredient 1: trend in woody carbon stocks over time
  4. 4. 1. Landcover issues for TREDD ❖ Existing global biomass maps inaccurate in woodland ecosystems by a factor of 2 (Hill, Ryan, et al, 2013). And, only 1 time period ❖ land cover change data only describes deforestation, not degradation (e.g. Hansen or in most part FAO FRA). ❖ creating consistent time series of land cover data in seasonal woodlands (e.g. with Landsat) is extremely challenging - when comparing over time, classification errors are greater than the change you are looking for McNicol, Ryan, in prep Deforestationrate(%) FAO FRA Hansen et al radar-based
  5. 5. TREDD approach: radar based biomass maps ❖ radar backscatter is an indirect measure of woody biomass in woodlands ❖ needs field data for calibration ❖ data available from 2007-10, and 2014 onwards ❖ method developed and tested in central Mozambique ALOS PALSAR L-band radar Ryan et al, 2012 Glob. Change Biol. Radar backscatter (m2/m2) woodybiomass groundmeasurement tC/ha
  6. 6. Afforestation! Degradation! Deforestation! Total! -200! -150! -100! -50! 0! 50! 100! Biomass loss (GgC)! Clearance of forest (farming) Extraction of biomass (fuel, timber) Fallow regrowth errorbars show 1 standard deviation from the 30,000 bootstraps Reduction in forest area Reduction in forest biomass density 2.3±1.5 % biomass lost per year (Ryan et al, 2012, Global Change Biology)
  7. 7. Advantages of the approach ❖ No cloud contamination ❖ Spatially explicit biomass estimates (no land cover classes needed) ❖ Can detect small changes over large areas (low bias) ❖ First estimates of degradation losses in African woodlands ❖ Resolution (25 m) allows detection of most kinds of land cover change 0 0.50.25 Kilometers Change in biomass (2010 as % of 2007) 200 % 0 % 100 % 0 0.50.25 Kilometers Change in biomass (2010 as % of 2007) 200 % 0 % 100 %
  8. 8. Scaling up to the Beira Corridor ❖ tested at small scales (Gorongosa) and districts (Sussendenga) ❖ then to Sofala, Manica and Zambezia: the TREDD area ❖ currently for all of Southern African woodlands
  9. 9. Metric that combines deforestation and degradation: The area that has lost >50% biomass in 3 years (1km2 pixels) Loss rates from 2-4%/yr at district and provincial scale Patchy! !(!( !( !( !( !( !( !( !( !( !(!( !(!( !( !( !( !(!( !( !( !( !(!( !(!( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !(!( !( !( !(!(!( !( !( !( !( !( !( !( !( !( !( M A L A W IM A L A W I Z I M B A B W EZ I M B A B W E G A Z AG A Z A I N H A M B A N EI N H A M B A N E M A N I C AM A N I C A N A M P U L AN A M P U L AN I A S S AN I A S S A S O F A L AS O F A L A T E T ET E T E Z A M B E Z I AZ A M B E Z I A TETE CHIMOIO BEIRA QUELIMANE Biomass loss Area affected over 3 years 20% 0%
  10. 10. McNicol et al, in prep Biomassloss(areaaffectedover3years,%)
  11. 11. 2. Causes of land cover change ❖ ingredient 2: data on which activities lead to biomass loss
  12. 12. 2a 2b 2c 1a 1b 1c 3a 3b 3c 2a 2b 2c 1a 1b 1c 3a 3b 3c 2a 2b 2c 1a 1b 1c 2a 2b 2c 1a 1b 1c 2a 2b 2c 1a 1b 1c bar = 500 m Radar change map high-res optical ground truth Ryan, et al (2014), Applied Geography
  13. 13. linking activities to biomass loss !1# !0.8# !0.6# !0.4# !0.2# 0# !Small!Scale!Agriculture!! !Construc2on!ac2vi2es!! !Charcoal!! !Logging!! !Large!Scale!Agriculture!! Carbon!loss!over!3!years!(TgC)! C!loss!by!land!use!ac2vity!❖ Small scale agriculture: 46±17% of biomass loss ❖ Biomass loss: 44±26% deforestation vs 56±33% degradation Ryan, et al (2014), Applied Geography
  14. 14. 3. How can this data be used to create baselines? ❖ crystal ball ? ❖ land use change modelling? ❖ “Despite the sophistication of our projection, it is slightly less accurate than if we had assumed no forest-cover change over 2000–2008” (Sloan and Pelletier, 2012, using GEOMOD) ❖ Ingredient 3: Scenarios and horizon scanning (futures research)
  15. 15. Scenarios built on driver-activity linkages Activity Driver Small scale agric Total Population Charcoal Urban Pop Logging Export of timber Construction etc Rural Pop Large scale agric Planned expansion 2000 20501950 2100 Data from INE (2012), and Global Timber (2011)
  16. 16. Assume cause-driver link constant BAU (existing drivers) New Drivers??
  17. 17. Lessons learned: scenarios ❖ the existing drivers are accelerating - so BAU is not linear; simple historical extrapolations are risky ❖ new driver on horizon is commercial agriculture - very uncertain rates and locations
  18. 18. Lessons learned: land cover change ❖ existing land cover data is not v. informative - esp re degradation ❖ Currently used deforestation rates (0.7% for Manica) are much lower than observed biomass loss rates (2.8±1.9%) ❖ degradation accounts for around ~50% of biomass loss ❖ patchy nature of land cover change means wall-to-wall mapping is needed !(!( !( !( !( !( !( !( !( !( !(!( !(!( !( !( !( !(!( !( !( !( !(!( !(!( !( !( !( !( !(!( !( !( !( !( !( !( !( !( !( !(!( !( !( !( !(!(!( !( !( !( !( !( !( !( !( !( !( M A L A W IM A L A W I Z I M B A B W EZ I M B A B W E G A Z AG A Z A I N H A M B A N EI N H A M B A N E M A N I C AM A N I C A N A M P U L AN A M P U L AN I A S S AN I A S S A S O F A L AS O F A L A T E T ET E T E Z A M B E Z I AZ A M B E Z I A TETE CHIMOIO BEIRA QUELIMANE Biomass loss Area affected over 3 years 20% 0%
  19. 19. casey.ryan@ed.ac.uk ❖ all of the TREDD team, for fruitful discussions and collaborations ❖ PhD students: Yaqing Gou, Daniel Jones ❖ Researchers: Iain McNicol, Neha Joshi, Nick Berry ❖ Funders: JAXA, ESA, IIED, NORAD, Norwegian embassy in Maputo Thanks!
  20. 20. Hill, …, & Ryan (2013) ground-based plus radar global maps
  21. 21. Metric that combines deforestation and degradation: AL, the area that has lost >50% biomass in 3 years (1km2 pixels) Loss rates from 2-4%/yr Patchy!
  22. 22. Large assumption! Change in urban pop (2007-10) Biomass lost due to charcoal (2007-10) Change in urban pop (2010-20) Biomass lost due to charcoal (2010-20) = etc for all drivers....
  23. 23. 5.3 3.8 7.2 Loss, TgC (2010-2020) Cause - driver linkages held constant Cause-driver linkages modified Ryan, et al (2014), Applied Geography

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