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2111 2005 Dual discounting in forest sector climate change mitigation Hanne K. Sjølie Greg Latta Birger Solberg Forest sector modeling workshop Nancy, France May 31, 2012

2111 2005 Dual discounting in forest sector climate change mitigation Hanne K. Sjølie Greg Latta Birger Solberg Forest sector modeling workshop Nancy,

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Page 1: 2111 2005 Dual discounting in forest sector climate change mitigation Hanne K. Sjølie Greg Latta Birger Solberg Forest sector modeling workshop Nancy,

21112005

Dual discounting in forest sector climate change mitigation

Hanne K. Sjølie

Greg Latta

Birger Solberg

Forest sector modeling workshop

Nancy, France

May 31, 2012

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Outline

Discounting in climate policy analyses / forest sector

Hypothesis

Model

Results

Discussion

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Basis for discounting

Social opportunity costs (SOC): Costs of capital

Social time preference (STP):

– per capita economic growth (g),

– the elasticity of marginal utility of consumption (η) and

– pure time preference (“impatience” of individuals) (p)

– STP = g×η + p

”Should be” the same, but differ due to i.a. taxes, externalities, information

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Discounting in climate policy analyses

The discount rate is very important in climate policy analyses

However, among scientists there are large disagreements regarding the magnitude of the discount rate as well as the rationale of the appropiate rate

Ex. Stern Review and the following debate:

The Review advocates for strong, rapid mitigation action as the benefits of action greatly exceed the costs

The conclusions diverge from many other economic assessment of climate policies

Moreover, “the difference stems almost entirely from its technique for calculating discount rates and only marginally on new science or economics” (Nordhaus, 2007, p. 201).

The Review used a discount rate of 1.4%4

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Low and dual discount rate

Stern (and many others) use arguments as ethics / intergenerational equity as arguments for using a low discount rate

Discounting environmental and non-environmental goods likewise is based on the assumption of perfect substitutability

Kula and Evans (Kula, E., Evans, D., 2011. Dual discounting in cost-benefit analysis for environmental impacts. Environmental Impact Assessment Review 31, 180–186) argues for the use of dual discount rate: One for monetary values and a lower for carbon

Their argument being as the scarcity of environmental values increases with economic growth, such values should not be included in the economic growth part of the STP

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Dual discounting in forestry

Kula and Evans compare the NPV of a forestation project in Nothern Ireland using hyperbolic discount rate starting at 3.5% for all values with a dual discounting scheme where monetary values discount rate starts at 3.5% and carbon at 1.5%

The NPV of the project is negative with the single discount scheme and positive with the dual

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Hypothesis

Do the results of Kula and Evans hold in all kinds of carbon mitigation projects in forestry?

More specifically, do the results hold in projects with an initial carbon stock?

Or could a low discount rate lead to initial harvests being offset by later carbon sequestration to a higher degree, thereby leading to less short-term carbon sequestration?

Hypothesis: When having initial carbon stocks, a lower discount rate on carbon yields less CO2 emission reductions in the short run

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Analysis

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Using a partial equilibrium model of the Norwegian forest sector

Carbon discount rates: 0%, 2%, 4%, 6% and 8%

Monetary discount rate: 4%

Carbon price: 12.5 €/ton CO2eq

Discount rate and carbon price are constant over the horizon

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The forest sector model for Norway NorFor

Demand for final products (county)

Forest growth, management:Biomass supply(9000 NFI plots)

Forest industrySawnwood (county) Pulp, paper and boards (mill) Bioenergy (county)

Trade(counties + 2 foreign regions)

Decay, machines

Growth

Transport

Substitution, storage

Combustion

Processing

Demand

GHG

Forest growth, management:Biomass supply

Forest growth, management:Biomass supply

Demand

Forest industry

Trade

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NorFor

Perfect foresight

Rational agents: consumers, industry, forest owners

Elasticity of foreign supply: 0.8 (logs), 5 (products)

Elasticity of foreign demand: -0.8 (logs), -5 (products)

20 5-year periods run, 19 analyzed

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Impacts on harvest

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Investment in forestry

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Industrial production

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Decline in the long run

Increase in the long run

Only marginal impacts with

discount rate >= 4%

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GHG fluxes

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GHG fluxes

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Discussion

Not discounting carbon yields lower GHG emission reductions in the short term but considerably higher in the long term

Carbon price harvest is below Base levels for all periods with a single discount scheme

Short-term harvests are higher with zero carbon discount rate than in both Base and 4% carbon disccount rate but considerably lower in the long run

Future carbon sequestration offsets early harvest to a higher extent with low carbon discount rate

Much more investments in forestry with low discount rate

Large shifts in industry with low carbon discount rate as NPV of substitution effects becomes relatively larger than producer surplus

Leakage is substantial particularly under low carbon discount rate but direction of results still hold with fixes trade levels

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Discussion

Discounting carbon less with the aim to allocate more resources to climate change mitigation does not necessiraly yield the desired results

Main difference from the Kula and Evans study is the initial carbon stock

Important to test a new scheme on a varity of assumptions

Basic assumption of dual discounting: non-substitutable goods

Instead of dual discounting, future scarcity of environmental goods can be reflected in increasing prices – but prices can be difficult to assess due to lack of markets

Discounting in models: Market observations or policies or ethical judgements? Versus other parameters in the models

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Thank you!

[email protected]