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Forest Conservation and CO2 Emissions: A Viable Approach

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Abstract

We adopt viability theory to assess the sustainability of the world’s forests while taking into account some of the competing economic, social, and environmental uses of these forests, namely, timber production, poverty alleviation through agriculture, and air quality as well as the negative externalities that these uses create. We provide insights on the different trade-offs faced to achieve sustainability and draw some policy implications as to what is the path leading to sustainability in the long run.

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Notes

  1. Conquerable land can be broadly defined as the land that is suitable for forest colonization. In our case conquerable land is proxied by world total forest surface prior to industrialization.

  2. All parameters values and references used to obtain them are provided in the Appendix.

  3. For simplicity land use change emissions have been neglected in this paper.

  4. See, e.g., Norby et al. [29].

  5. Van Soest and Lensink [38] set δ = 1.

  6. Note that P A , unlike the price of timber P, is constant. In fact, our model accounts for all wood production and it makes sense to have a variable P. On the contrary, the agricultural production in our model represents only a fraction of world agricultural production. For this reason,we make the simplifying assumption that P A is constant.

  7. Note that F min = 0 has to be seen as a physical constraint and we, by no means, think that a world without forests is sustainable.

  8. The selection of the lower and upper bounds for each state variable is further discussed in the Appendix.

  9. Recall that F min = 0.

  10. Note that, for the time being, T is kept constant and equal to zero.

  11. The term economic crisis is used here to denote the non fulfillment of one or more of the economic constraints.

  12. Note that φ·F max + W = 17.5 GtCO2. Current world emissions are far from these Figures. This rules out scenario E2 as an alternative.

  13. As we saw, increasing forest surface beyond \(\overline{F}\) entered in contradiction with the satisfaction of our revenue constraint (12).

  14. See http://www.reuters.com/article/environmentNews/idUSN0142868820080801.

  15. See http://www.alertnet.org/thenews/newsdesk/N16494217.htm.

  16. Source: http://www.geo.vu.nl/~renh/deforest.htm

  17. Source: EIA [14].

  18. Source: NOAA [28].

  19. Source: Bernstein et al. [7] and EIA [14].

  20. Most elasticity values are comprehended between −0.25 and −0.75.

  21. See e.g.: www.villageprojectsint.org and www.edenprojects.org.

  22. www.bber.umt.edu/pubs/forest/prices/loggingCostPoster.pdf

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Acknowledgements

We wish to thank the two anonymous reviewers and the associate editor for their very helpful comments. We want to thank Vimades Inc. for sharing with us their software to run the Viability Kernel Algorithm, and Lucía Andrés Domenech for her help in producing the figures. Research supported by NSERC, Canada, FQRSC, Québec, and A.N.R. “Agriculture et Développement Durable”—DEDUCTION.

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Correspondence to Georges Zaccour.

Appendix: Variables Description

Appendix: Variables Description

We provide in this appendix details regarding the construction and measurement of the model's variables and the estimation of parameters' values.

1.1 State Variables

F :

Forest Surface

Forest surface in the world measured in hectares. The current stock of forest is estimated by FAO [19] at 3,952 million ha in 2005. Parameter F max has been estimated for 1750 AD at 42% of the globe's surfaceFootnote 16 (i.e., 13,067 million ha excluding Antarctica and Greenland). This gives us a value for F max of approximately 5,500 million ha. Consequently, we require that \(F_{t}\in \left[ F_{\rm{min}}, F_{\rm{max}}\right] =\left[ 0\cdot 10^{9}\text{~ha}, 5.5\cdot 10^{9}\text{~ha}\right] \).

E :

Yearly emissions of CO2

These are world yearly emissions of CO2 measured in metric tons. In 2005, total CO2 emissions amounted to 28.2 Gtons.Footnote 17 Minimum emissions are set to equal 1990 emission levels, i.e., 21.4 Gtons. The value of maximum emissions used plays a minor role. It has been set to equal the double of 1990 emissions. The reason to choose a maximum is simply the need to have bounded states. Hence, the constraint reads E t  ∈ [ E min,E max] = [21.4 Gtons CO2, 42.8 Gtons CO 2].

S :

Cumulated Quantity of CO2 in the Atmosphere

The cumulated stock of carbon in the atmosphere is measured in gigatons. The atmospheric stock of carbon has been estimated to be approximately equal to 800 Gtons CO in 2005. The current concentration of carbon measured in parts per million was approximately 379 ppm in 2005.Footnote 18 The upper bound value is set at 650 ppm i.e., 1,372 Gtons CO. The lower bound has a negligible impact on the solution. We have set it at preindustrial levels, that is 284 ppm (i.e., roughly 591 Gtons CO) in year 1832. In short, we want S t  ∈ [ S min,S max] =[591 Gtons CO, 1,372 Gtons CO]≡ [2,167 Gtons CO2, 5,031 GtCO2].

1.2 Control Variables

ρ :

Yearly Reforestation \([\rho _{\rm{min}},\rho_{\rm{max}}]=[0\cdot 10^{6},\;3\cdot 10^{6}]\)

For the period 1990–2005, FAO [19] estimates world yearly reforestation at 2.8 million ha. We let reforestation vary between no reforestation and 3 million ha/year.

d :

Yearly Deforestation \([d_{\rm{min}},d_{\max}]=[0\cdot 10^{6}, 15\cdot 10^{6}]\)

For the same period, FAO [19] estimates the average global deforestation rate at 13 million ha/year. We let deforestation vary between zero and 15 million ha/year.

v :

CO 2 Emissions Adjustment Rate [v min,v max] = [ − 0.015, 0.03]

During the decade going from 1990 to 2000 world's CO2 emissions increased at roughly 1%/year.Footnote 19 Only a few countries like Germany, United Kingdom, Denmark, Finland, some Eastern European countries, and former Soviet Republics were able to reduce their emissions. In particular, Germany achieved a 1.8% yearly cumulative decrease. On the other hand China's emissions increased at a rate of 3% per annum. All the other big economies lie somewhere in between. Between 2000 and 2008, however, world emissions have increased at a faster rate, 3.4% year − 1, [24] with a probable decrease during the next 2 years (2009--2010) due to the world crisis. Following these observations we have set both the lower and upper bounds on v. As a benchmark scenario we have chosen v ∈ [v min,v max] = [ − 0.015,0.03].

T :

Monetary Transfers

Monetary transfers to forest owners expressed in 2005 US dollars. Unless otherwise specified, transfers are set constant and equal to zero, T = 0.

1.3 Other Parameters

η :

Natural Growth Rate of the Forest

FAO [19] gives estimates of net yearly afforestation (5.7 million ha) of which a fraction is due to human reforestation and the rest belongs to the natural renewal of the forest. Human reforestation ρ is estimated at 2.8 million ha, meaning that the term \(\eta \cdot \left( 1-\frac{F}{F_{\rm{max}}}\right) \cdot F\) has been, on average, equal to 2.9 million ha during this period. If we substitute F by its value for the last years and F max by the value pointed above we obtain η = 2.61·10 − 3.

φ :

Carbon Absorption Rate by Forests

This parameter is measured in metric tons of CO2 equivalent absorbed per hectare of forest per year. According to Le Quéré et al. [24] during the decade from 1990--2000 forests absorbed 2.6 PgC year − 1 (i.e., 2.6 Gtons CO) which amounts to 9.53 Gtons CO2. Considering that world total forest surface equals 3,952 million ha, we can estimate average yearly carbon sequestration at 2.412 tons of CO2 ha − 1 year − 1.

W :

Carbon Absorption Rate by Oceans

Accounts for the amount of carbon absorbed by oceans every year. According to Le Quéré et al. [24], the oceans were able to sink on average 2.2 PgC year − 1 for the period 1990--2000, this is equivalent to 8.07 Gtons CO 2 year − 1.

\(\underline{R}\) :

Minimal Revenue of Land Owners

Measured in US dollars. We denote \(\underline{R}\) as the current or status quo revenue. We compute \(\underline{R}\) by substituting in Eq. 9 the current values of all the variables and parameters in our model.

\(\underline{q}\) :

Minimum Timber Supply

Minimum timber supply is measured in m3 of timber per year. Current timber supply is estimated by FAO [19] equal to 1,623 million m3 year  − 1 of industrial roundwood and 1,777 million m3 year − 1 of fuelwood. We estimate minimum timber supply to be equal to current timber supply, i.e., 3,400 million m3 year − 1.

n :

Timber Yield

The timber yield is measured in m3 ha1 year1. We use the average world Figures given by FAO [19], i.e., n = 110/ha of growing stock.

β :

Lower Productivity due to Forest Depletion

Lower agricultural yield measured in tons per hectare. Eswaran et al. [15] estimate the loss in productivity as a consequence of land degradation, erosion and desertification. They report that the productivity loss due to such processes in Africa ranges between 2% and 40% and provide an average estimate for the whole continent to be equal to 8.2% in average. If average productivity is \(\overline{Z}\) then β is equal to 0.061.

γ :

Selective Logging Yield, Fraction of Average Yield

The selective logging yield is measured as a fraction of average yield. When forests are managed for wood production they produce as much as 1--3 m3/ha (in other words n·γ = 1 − − 3 m 3). We have set the value of γ = 0.015.

δ :

Fraction of Forests Selectively Logged

Share of the world's forests selectively-logged. Following FAO [19], parameter δ has been calibrated at 30% (i.e., δ = 0.30) to fit the world yearly production of wood q.

θ :

Slope of Wood Demand

According to FAO [19], the commercial value of all wood (i.e., roundwood and fuelwood) in 2005 was $64 billion/year of which only 7 billion correspond to fuelwood. World production equals 3,400 million m3. The average price for both types of wood is $18.8/m3. FAO [16] gives the elasticity of demand for several countries and several types of wood.Footnote 20 A representative value of both the mean and median price elasticity of wood is −0.50. We have approximated an iso-elastic curve by a linear one in an interval of 2,000 million m3 centered at 3,400 million m3 such that the average elasticity inside the interval equals −0.50. The slope of our demand can be then computed accordingly to obtain θ = − 2.7·109.

\(\overline{P}\) :

Choke Price of Wood

With the average price of wood and the slope of demand computed above, we can retrieve the choke price of our inverse demand function and obtain \(\overline{P}=27.98\) (US $/m 3).

ψ :

Extra Productivity of Deforested Land

Parameter ψ denotes the productivity gain of land after deforestation. It is measured as a fraction of average productivity. A reasonable range for ψ suggested in the literature is 0.2 − 0.5. We adopt ψ = 0.3.

κ 1 :

Per-Hectare Reforestation Cost

Parameter κ 1 denotes the reforestation cost per hectare of forest. According to the World Bank the cost for seedling is roughly $40 per thousand seedlings and the number of seedlings per hectare is equal to approximately 2,000. This amounts to approximately $80/ha of forest just for seedling. Reforestation costs, however, also include other costs such as labor costs that change with countries. The World Agroforestry Centre gives estimates for the Philippines around $1,000/ha, other NGO organizations provide estimates that range between $180/ha for Senegal and $400--500/ha for other countries in Africa such as Sudan, Madagascar and Ethiopia.Footnote 21 We have chosen the round value of $500/ha that is representative of the average cost taking these different observations.

κ 2 :

Per-Hectare Deforestation Cost

Parameter κ 2 denotes the deforestation cost per hectare of forest. The Bureau of Business and Economic Research of Montana University estimates the costs of ground-based logging to be equal to $22.70 for every green ton of harvest for the year 2006.Footnote 22 Considering that a green ton is equivalent to 2,000 pounds of undried biomass material (i.e., 907 kg) and that the density of wood is typically 500 kg/m3, then for a representative douglas fir plantation (530 kg/m3), we obtain that the deforestation cost is equivalent to $13.26/m3. If the yield per hectare is equal to 110 m3/ha, then we obtain an estimate of the deforestation cost per hectare of $1,459/ha.

P A :

Average Price of Representative Agricultural Product

Measured in US dollars per metric ton. To determine the average price of the representative agricultural good, we took four representative commodities (i.e., cocoa, coffee, cotton, and sugar) from FAO [18]. Coffee and sugar in Brazil and Latin America and cotton and cacao in Africa are four crops that are related with deforestation processes. The net economic yield per hectare of crop ranges from $1,660/ha for coffee to $771/ha for cocoa. The average yield equals $1,141/ha. We have chosen the price of cotton to be the representative price of the agricultural good since its prices and economic yield ($1,467 per metric ton and $1,088/ha) are the closest to the mean.

\(\overline{Z}\) :

Average Land Productivity

Measured in tons per hectare. The average yield has been computed taking into account the yield of those same four crops in metric tons per hectare and annum as mentioned before. The estimated annual yield per hectare is equal to 0.742 metric tons/ha.

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Domenech, P.A., Saint-Pierre, P. & Zaccour, G. Forest Conservation and CO2 Emissions: A Viable Approach. Environ Model Assess 16, 519–539 (2011). https://doi.org/10.1007/s10666-011-9286-y

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