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296 | IAASTD Global Report
than for cereals alone. Across the assessments, the area in crop production increases from 1.5 billion ha (or 11% of the earth's land surface) to 1.60 to 1.77 billion ha. As indicated by FAO, this expansion is within the scope of total land available for crop production. The fact that the assessments considered here agree on a rather flexible continuous response of the agriculture system to demand increases is interesting, as more skeptical views have also been expressed. An important implication, however, is further loss of the area available to unmanaged ecosystems |
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with further integration of crop and livestock enterprises in many places. Strong growth is implied for confined livestock production systems; in the FAO scenario at least 75% of the total growth is in confined systems, although there are likely to be strong regional differences (e.g., less growth of these systems in Africa). This is a continuation of historic trends. The major expansion in industrial systems has been in the production of pigs and poultry, as they have short reproductive cycles and are more efficient than ruminants in converting feed concentrates (cereals) into meat. Industrial enterprises now account for 74% of the world's total poultry production, 40% of pig meat and 68% of eggs (FAO, 1996). At the same time, a trend to more confined systems for cattle has been observed, and a consequent rapid increase in demand for cereal- and soy-based animal feeds (these trends are included in the projections discussed in the previous subchapter) (see Delgado et al., 1999). Finally, while there are good economic arguments for the concentration of large numbers of animals in confined systems, there can be significant impacts on surrounding ecosystems, something that is only recently started to be assessed in sufficient detail in agricultural assessments. The effects primarily involve N and P cycles. While some types of manure can be recycled onto local farmland, soils can quickly become saturated with both N and P since it is costly to transport manure. Forestry. The FAO assessment pays considerable attention to forestry and the outlook for forestry, but mostly in a qualitative way. The MA also considers the future of forestry, but focuses more on the extent of natural forests than the development of forestry as a production system (although some data is available). Overall, both assessments agree on that the general trend over the last decades of a decreasing forest resource base and an increasing use of wood products will continue. Important driving forces for forestry include demographic, sociopolitical and economic changes, changes in extend of agricultural land, and environmental policy. Both population and economic growth affect forestry directly via an increase in demand for wood and indirectly via the impact on agricultural production. There is strong evidence that with rising incomes, demand for forest products increases, especially for paper and panel products. The increasing demand for wood products is also assumed in the scenarios of the FAO and MA (Figure 4-35). The demand for industrial roundwood is expected to increase by about 20-80%. The lowest projection results from the Technogarden scenario (assumes a high efficiency of forest utilization in order to protect forests) while the highest projection results from the Global Orchestration scenario (reflecting the very high economic growth rate). The use of wood products as a source of energy (fuel-wood) is not expected to grow fast, and may even decline. The use of fuelwood is particularly important at lower incomes; wealthier consumers prefer and can afford other forms of energy. As a result, fuelwood consumption is a function of population growth (increasing fuelwood demand) and increased income (decreasing demand), with the net results being a small decline and rise over the next 30 years. The impact of environmental policies on forestry may |
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