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JOHN ANTLE, SUSAN CAPALBO, SIAN MOONEY Departm ent of Agri cu!tural Economi cs and Eco nom ics, M ontana State Un iversity M any industrial- C credits at a cost that annual increase ized counties are is economically compet- in C resulting looking at ways itive with other so urces. ftom a change to croppmg systems Recent research suggests that U.S. emissions could to reduce their net emissions of greenhouse gases such as carbon dioxide. The Kyoto be reduced by up. to 8 percent protocol of the United thtough sequestering C in agricul- Nations Framework (Ural soils (Lal et al.1998) . Soil C can be increased by adopting Convention on Climate Change inuo- that increase biomass production in six different "agroecozones" within Montana. C estimates are predicted using the Century ecosystem duces the idea of a C (carbon) credit management practices that reduce soil model (Antle et al. 2001). Figure 1 trading scheme that would give credit disturbance (and thus C oxidation) shows that the quantity of C sequestered to participating countries for reducing and/or increase biomass production. A varies across space, thus all management emissions domestically or purchasing mix of practices is likely under a market practices are not equally suited to each them internationally. This potential for C reflecting the spatial variability of area. Based on Figure 1, ecozone 58a- new market could be beneficial to agri- resource endowments and economic high has tl1e greatest technical potential cultural producers if they can provide considerations. Figure 1 presents the to sequester soil C. Examining only tl1e technical potential ignores a key eco- Figure 1. Average annual rate of carbon accumu lation for selected crop system changes that increase biomass (Century ecosystem model) nomic question: what level of incentive or compensation is required to encourage producers to adopt practices tl1at increase soil C? A producer will participate in a policy or market to sequester additional C if the net returns from production 0.8 .. .. -c QJ c.s ~~QJ 0.6 ::::J 0' .. QJ c.s U') ~ .. 0.5 u C QJ 0 __ :r: .0 VI changes plus tl1e market value of C 0.7 QJ • 53a high produced exceed the net returns from • 53a low existing production practices. Figure 2 • 58a high • 58a low presents C supply curves for each region, reflecting the opportunity COSt 0,4 c.s C per metric ton of C incurred by pro- ~ ~ 0.3 c.s u C 0';:; '.;:i ducers tl1at swi tch to a system that .- Q) :o~ 0.2 sequesters additional soil C. -c « 0.1 0 For example, 3 million metric tons SF-WF SF-WF SF -GR SF -SR SF-WR 24 C H O I C ES Fall 2002 SF-GR Spring Spring Spring Spring wheat wheat wheat wheat fallow fallow fallow fallow SF-SR to to to to SF-W R winter wheat fallow grass continuous spring wheat continuous winter wheat of C can be supplied from ecozone 52high for approximately $45 per metric ton, while the same quantity in ecozone 58a-high could be supplied for approximately $60 per meuic ton. Figure 2. Supply of carbon at payments ranging between $10 to $100 per metric ton lW~----------------------------~==~ . 52 high . 52 low 100 c • • • • ~ u EC!> 2; ~ 80 53a hilJh 53a low 58a high 58a low Figure 3. Proportion of eligible land area entering a carbon payment program at payments ranging between $10 to $100 per metric ton lW ~~~==~--------------------------c 100 . 52 high . 52 low BO • 53a high • 53a low • 58a high r - - - - - - - - - -f--+f--+>H - - ~ -EC!> • 58a low 2; bO ~ C!> bO C!> D- c. ~ 40 ~ (5 0 Vl ~ 40 (5 0 W 0 0.0 W 05 1.0 15 2.0 25 3.0 35 4.0 45 5.0 00.0 u ~ Addit ional Carbon (Mi llion Met r ic Tons ) u u ~ U U M U Proportion of Area Entering Payment Program Figure 2 demonsrrates that the efficien- tions that vary by location have two and Economics, Montana State cy of so il C sequestration varies spatial- imporrant implications. First, a market University, Bozeman, 2001. ly and is dependent on both the bio- for C will be beneficial ro regions that physical rates of C accumulation and have tile lowest opporrunity cOSts per Intergovernmental Panel on C limate the site-specific opportunity costs of metric ron of C sequestered, and as the Change (IPCC). Land Use, Land-Use changing production practices. demand for C increases, there will be Change, and Forestry. A special report of the Intergovernmental Panel on Climate Change. R.T. Watson, LR. Noble, B. Figure 3 shows that as the price per more opporrunities for more producers metric ron of C increases, parricipation to in C sequestration also increases. enter tile market. Second, C can be sequestered in agricultural soils of the Bolin, N.H. Ravindranath, D.]. T hese shares are simulated using a Northern Great Plains at a cost compet- Verardo, and D.]. Dokken, eds. model for dryland grain production in itive with other sources. Related work Canlbridge: Cambridge University Montana (An tle et a1. 2001). The by Stavins (1999) and IPCC (2000) Press, 2000. model reflects both site-specific net show tllat forest practices can sequester returns and the biophysical potential C at costs that range from $3 per metric LaI, R. , L.M. Kimble, R.F. ro sequester C. At low payment levels, ton to over $100 per merric ton. These Follert, and C.V Cole. The only producers with the lowest oppor- figures suggest that C sequesrration tunity cost per metric ron C will par- could provide new economic opportuni- ticipate. As payments increase, produc- ties for U.S. agricultural producers. Potential of U S. Cropland to Sequester C and Mitigate the Greenhouse Effect. Chelsea, MI: Ann Arbor Press, 1998. ers with higher opportuni ty cos ts can enter the market increas ing the percentage of producers and land area that are engaged in the market and the benefits that accrue ro agriculture. Impli cations for agriculture Biophysical and economic condi- For More Information Antle, ].M., S.M. Capalbo, S. Mooney, and K.H. Paustian. "Spatial heterogene- Stavins, R.N. 1999. "The costs of carbon sequestra- ity, contract design and the efficiency of tion: A revealed-preference carbon sequestration policies for agri- approach. " Amer. Econ. culture." Draft working paper. Rev. 89(September Department of Agricultural Economics 1999):994- 1009. Fall 2002 CH O I C ES 25