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Emissions Scenarios - IPCC

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Summary Discussions and Recommendations 303<br />

to cropland and energy biomass and 20% to forests at the top,<br />

60% to forests and 40% to other categories (including<br />

grasslands) to the left, and 80% to other categories (including<br />

grasslands) to the right.<br />

In most scenarios, the current trend of shrinking forests is<br />

eventually reversed because of slower population growth and<br />

increased agricultural productivity. Reversals of deforestation<br />

trends are strongest in the В1 and A1 families. In the В1 family<br />

pasture lands decrease significantly because of increased<br />

productivity in livestock management and dietary shifts away<br />

from meat, thus illustrating the importance of both<br />

technological and social developments.<br />

The main driving forces for land-use changes are related to<br />

increasing demands for food because of a growing population<br />

and changing diets. In addition, numerous other social,<br />

economic, and institutional factors govem land-use changes<br />

such as deforestation, expansion of cropland areas, or their<br />

reconversion back to forest cover (see Chapter 3). Global food<br />

production can be increased, either through intensification (by<br />

multi-cropping, raising cropping intensity, applying fertilizers,<br />

new seeds, improved fanning technology) or through land<br />

expansion (cultivafing land, converting forests). Especially in<br />

developing countries, there are many examples of the potential<br />

to intensify food production in a more or less écologie way<br />

(e.g. multi-cropping; agroforestry) that may not lead to higher<br />

GHG emissions.<br />

Different assumptions on these processes translate into<br />

altemative scenarios of future land-use changes and GHG<br />

emissions, most notably COj, CH^, and NjO. A distinguishing<br />

40% 50% 60% 70% 80%<br />

Other (ind. grasslands)<br />

Figure 6-4: Global land-use pattems, shares (%) of croplands and energy biomass, forests, and other categories including<br />

grasslands - historical development from 1970 to 1990 (based on Bl-IMAGE) and in SRES scenarios. As for the energy<br />

triangle in Figure 6-3, each comer corresponds to a hypothetical situation in which land use is dedicated to a much greater<br />

extent than today to one category - 60% to cropland and energy biomass at the top, 80% to forests to the left, and 80% to<br />

other categories (including grasslands) to the right. Constant shares in total land area of cropland and energy biomass, forests,<br />

and other categories are denoted by then respective isoshare lines. For 1990 to 2100, altemative trajectories are shown for the<br />

SRES scenarios. The three marker scenaj-ios AlB, Bl, and B2 are shown as thick colored lines, and other SRES scenarios as<br />

thin colored lines. The ASF model used to develop the A2 marker scenario projects only land-use change related GHG<br />

emissions. Comparable data on land cover changes are therefore not available.The trajectories appear to be largely model<br />

specific and illustrate the different views and interpretations of future land-use patterns across the scenarios (e.g. the scenario<br />

trajectories on the right that illustrate larger increases in grasslands and decreases in cropland are MiniCAM results).

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