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Effect of Biofuel on Agricultural Supply and Land Use

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Handbook of Bioenergy Economics and Policy: Volume II

Part of the book series: Natural Resource Management and Policy ((NRMP,volume 40))

Abstract

While biofuels were introduced, in part, to reduce greenhouse gas emissions through replacing fossil fuels, comparing their impact to conventional sources has been difficult. This is largely due to the challenges of quantifying indirect land use change due to biofuels, which has proved controversial. This paper introduces a stylized, dynamic framework to analyze the evolution of land use expansion as well as deforestation over time. Our analysis suggests that land use change is a dynamic process and that relationships between variables are not regular over time and space. Technological change and effective environmental policy, of both agriculture and forests, can curtail deforestation. Outcomes of the model are illustrated with empirical data from the U.S. and Brazil. In the United States, deforestation does not lead directly to cropland expansion, as there is a transition period during which land is used as pasture or left idle. In Brazil, with four times more land in pasture or underutilized land than in cropland, there is significant potential for cropland expansion from this underutilized land.

History doesn’t repeat itself, but it rhymes

—Mark Twain

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Notes

  1. 1.

    They are regular in the sense that they produce outcomes that occur frequently under the same conditions (allowing some random errors that do not affect the average). For example, a constant elasticity reflects a regular relationship.

  2. 2.

    This distinction results from the Cambridge controversies (Cohen and Harcourt 2003). Xabadia, Goetz, and Zilberman (2006) derived such relationship with a dynamic framework—expanding on the original aggregation of Houthakker (1955).

  3. 3.

    Zilberman (2014) presents a framework for modeling agricultural systems that recognizes heterogeneity among producers, dynamic elements, and evolving pest damage.

  4. 4.

    Higher output price leads to lower gains from delaying the introduction of capital, since \( \dot{u}_{t} = (r + \gamma )u_{t} - p_{t} F_{{S_{t} }} \left( {X_{t} ,A_{t} ,S_{t} } \right) \) declines over time and investment become more valuable. The increase in output price has the same qualitative effect as a reduction in interest rate, namely increased investment.

  5. 5.

    Unless we are at a corner solution where all the land is in farming, as the increase in \( \beta \) is not sufficient to lead to conversion of land back from farming to wilderness.

  6. 6.

    In this case, there were political reasons for fast settlement.

  7. 7.

    There may be some GHG emissions from conversion of rangeland to cropland, but it depends on cultural practices (Lal 2002). For example, use of low or no tillage can minimize it, and in some cases can even help to rebuild the carbon stock in the soil.

  8. 8.

    For example, the banning of GMOs. Barrows et al. (2014) demonstrate how the introduction of GMOs actually reduce the carbon footprint of agriculture.

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Zilberman, D., Rajagopal, D., Kaplan, S. (2017). Effect of Biofuel on Agricultural Supply and Land Use. In: Khanna, M., Zilberman, D. (eds) Handbook of Bioenergy Economics and Policy: Volume II. Natural Resource Management and Policy, vol 40. Springer, New York, NY. https://doi.org/10.1007/978-1-4939-6906-7_7

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