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Gordon Smith
April 6-9, 20095th Forestry and Agriculture Greenhouse Gas Modeling Forum
Shepardstown, West Virginia
Leakage Accounting in Forestry and Agriculture
Outline
• Concepts, current practice & offset supply implications
• Needed research and modeling
Outline
• Concepts, current practice & offset supply implications
• Needed research and modeling
Leakage definition
• Displacement of emissions from project area to outside project acrea
Kyoto accounting: Increased emissions within the project boundary
• Caused by project activity
Cause of leakage
• If a project reduces supply of a good without reducing demand, the market will replace much of the lost supply
Leakage greater for smaller projects because no price increase decreasing consumption
• If replacement supply creates new emissions, leakage occurs
Emissions per unit of production may be higher, lower, or same as pre-project emissions
Factors affecting leakage rate• Project type/activity
• Project location
• GHG accounting rules
• Project size
• External economic changes
Example: FASOM GHG shows US forest management large sink or source across recent variation in agricultural product prices
Leakage by activity: Agriculture• Plowing to no-till: Little or none
May reduce yield in some situations, displacing production
• Reducing fertilizer use: Little or none
May reduce yield, displacing production
• Changing fertilizer use: None (possibly positive?)
• Changing manure management: None
Leakage by activity: Forestry• Avoided deforestation: High
• Forest management: DependsGenerally high if reduces harvest
May only shift emissions in time
May be negligible if harvest maintained
• Afforestation: DependsSignificant if causes clearing elsewhere
May be negligible if combined with forest management**EPA. 2005. Greenhouse Gas Mitigation Potential in U.S. Forestry and Agriculture, EPA 430-R-05-006.
Current treatment of leakage• Econometric estimates with cross-
sectoral interactions (EPA Climate Leaders)
• Address specific activities (CDM)
• Ignore (1605(b), RGGI)
• State that should be dealt with, but give no guidance (CCAR)
• Assign flat rate (VCS)
Leakage varies by program
Climate Leaders 40.6%
CCAR (proposed forestry rules)
24%
CCX Not addressed
RGGI Not addressed
CDM Grazing analysis
Florida afforestation example
Rules affect offset supply
• Reducing number of offsets credited increases cost of creating each offset
•Want policies to make actors responsible for their actions
Credit actual GHG benefits
Don’t credit actions without GHG benefit
When GHG benefit occurs
• Current rules credit forest rotation extension with GHG benefit as carbon stock increases within project boundary
• Leakage indicates GHG benefit occurs when harvesting resumes
Credit actual GHG benefits
Don’t credit actions without GHG benefit
Credit timing effect
When award offset Management change commitment
Harvest resumption
Project years offsets accrue
11-20 35
Tons CO2e/acre credited 19.4 19.4Levelized $/ton CO2, Year 11
$9.17 $31.12
Florida: extend pine rotation 20 to 35 years
6% discount rate
Policy recommendations
• Assign low-leakage activities zero leakage rate
No-till, fertilizer N2O, manure management
• Deforestation fee (not offsets)
Applies to all conversions, including small areas
Fee set according to average carbon stock, by potential forest type and site productivity
Forest management• Determining project additionality and
baseline is problematic
Modeled baseline depends on wood product prices
• Cap sector, not voluntary opt-in
Baseline can be set at average carbon stock by forest type and site productivity, avoiding problems of modeling profit-maximizing management
Avoids additionality and leakage problems
Smaller ownerships more likely to sequester; need to identify how small to set property size threshold for inclusion in cap
Policy recommendations
• If forest management is capped, can assign afforestation zero leakage
Rewards entities that do good
• If no cap on forest emissions, more research is needed…
Outline
• Concepts, current practice & offset supply implications
• Needed research and modeling
Forest management research• US mapping of potential forest type and
site productivity
• Quantification of average carbon stocks, by forest type and site productivity
• Tool for overlaying map and land parcel boundaries to set baseline for each ownership
Forest management research 2• Decadal variation in C stocks at
property scale, relative to average
How long and how far do C stocks go below average because of normal harvest, and how does this vary by ownership size?
• Natural disturbance
How many ownerships go below average C stock because of natural disturbance, how far, and how does this vary by ownership size?
National-scale monitoring
• Needed for REDD
• Terrestrial C quantification protocols
For all land cover types
Must detect small % change
Must be repeatable
Must be do-able by developing countries
Desirable to be compatible with developed country methods
“Factoring out”
• Can carbon effects of natural disturbance be separated from effects of human actions?
Used retrospectively to determine compliance with REDD & A1 targets
Use to allocate REDD payments between entities that control lands and national governments
At minimum, inventory “unmanaged” forest
Global modeling
• How comprehensive must accounting be to avoid having to estimate leakage?
What other sectors should be addressed to limit leakage?
Which countries (for international leakage)?
Comprehensive accounting•What land types must be counted to
get realistic counts?
Peat estimated to be 6% of global emissions: how measure area and depth of loss?
Develop inexpensive protocols for non-forest lands
Avoid things like recent Russian claim of a new billion ton sink
REDD program design
•What are effects of alternative consequences for later reversal of REDD?
Cost in tons of emission
Cost in dollars to meet net emission target
Program evaluation
•What REDD programs work, and why?
• Do soil protection programs enhance soil carbon stocks?
• Do educational programs affect GHG emissions?
No-till, fertilizer management, water management
Model calibration
•What is correlation between actual behavior and profit maximizing behavior?
Necessary for constructing mitigation supply curves
Most important needs• Support comprehensive GHG
accounting
Methods for counting, esp. non-forest lands
Volatility of fluxes
• Address fears of cap on forests
Which landowners have deficits from natural disturbance, and for how long?
Show banking can cover normal management
Climate feedbacks on unmanaged forest
• REDD: effects of alternative consequences for reversals
Gordon Smith
Ecofor LLC206.784.0209
13047 12th Ave NWSeattle, WA 98177
USA
Thank you