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Emissions Scenarios - IPCC

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252 Emission <strong>Scenarios</strong><br />

In addition to their cumulative emissions, the scenario families<br />

are characterized by very different emissions trajectories. The<br />

AI fossil fuel scenarios have continuously increasing<br />

emissions, with rapid growth before 2050 and slower growth<br />

thereafter. The AI scenarios with the "balanced" energy mix<br />

(e.g. the marker AlB-AIM) typically have emissions that<br />

decline after 2050, while the AIT technology scenarios have<br />

slower growth prior to 2050, and a steeper decline after 2050.<br />

As for the Al fossil fuel scenarios, A2 family scenarios are<br />

characterized by high rates of growth in emissions prior to 2050<br />

and subsequently continued growth but at lower rates. Unlike<br />

the rest of the A2 scenarios, the A2-AI-MiniCAM has more<br />

rapid growth in emissions after 2050 than before 2050, because<br />

per capita incomes in a number of developing regions do not<br />

reach a level at which per capita energy demands rise rapidly<br />

until the middle of the 2Г' century. The Bl family is<br />

characterized by lower growth in emissions prior to 2050,<br />

mostly because of lower rates of growth in energy demand,<br />

followed by declining emissions after 2050. Finally, the B2<br />

family is characterized by relatively stable emissions post-2050,<br />

after roughly doubling emissions between 1990 and 2050.<br />

5.3.2. Land-Use Carbon Dioxide <strong>Emissions</strong><br />

Most changes in land use are induced by the demand for<br />

cropland and grassland, which is driven by the demand for<br />

food products, the extent of biomass energy use, and policies<br />

and practices associated with forest management. The 1990<br />

land-use COj emissions remain fairly uncertain, estimated at<br />

1.6 ± 1.0 GtC (Watson et a!., 1996a); a similar level of<br />

uncertainty is attached to current land-use emissions. This<br />

uncertainty is reflected by the quantification of the SRES<br />

storylines - the 1990 emission estimates from different models<br />

range between 1.0 and 1.6 GtC, while the spread of estimates<br />

at the four-region level is even larger. For the sake of<br />

comparabifity, common, standardized (see Box 5-1 on<br />

standardization) emissions are established at 1.1 GtC in 1990<br />

and 1.0 GtC in 2000, to reflect the net carbon flux from<br />

contemporary changes in forest cover.<br />

Generally, the SRES models use different approaches to<br />

estimate land-use change emissions - in some cases the only<br />

source of emissions is tropical deforestation, while in other<br />

cases more sources and sinks (including natural) are included.''<br />

Moreover, méthodologie differences and uncertainties in<br />

carbon content, carbon cycling, and land classification result in<br />

seemingly inconsistent results between models that cover the<br />

same land-use sources. These features complicate a<br />

straightforward comparison between land-use emissions in<br />

scenarios generated by different SRES models.<br />

' The most comprehensive treatment is embedded in the IMAGE<br />

model. For the sake of comparison the IMAGE team has made a<br />

tentative estimate of those (net) emissions that are reasonably<br />

consistent with what other models reported. These derived values are<br />

used in this report.<br />

Future trajectories of land-use COj emissions are shown in<br />

Figure 5-4. <strong>Emissions</strong> in the 40 SRES scenarios range widely<br />

in the same year and change significantly over time. In<br />

scenarios with continued deforestation, emissions rise initially,<br />

then reach a maximum, and finally decline with depletion of<br />

forestland that can be cleared. At the other end of the scenario<br />

spectrum, emissions turn negative and land-use changes<br />

become an increasing CO2 sink through afforestation. By 2020,<br />

the resultant uncertainty ranges between 0 and 3 GtC across all<br />

40 SRES scenarios with a median of I.l GtC. By 2050, the<br />

scenario range shifts to between -0.7 and 1.2 GtC (median, 0.5<br />

GtC). By 2100 the scenario range lies between -2.8 and 2.2<br />

GtC, with a median of 0.0 GtC. Interestingly, in specific years<br />

(e.g., in 2050) scenarios from аИ four SRES families fall within<br />

a relatively narrow emissions corridor (i.e. at least one scenario<br />

from each of the four SRES scenario families falls within the<br />

25"' and 75* percentiles of the emission range). This indicates<br />

that similar levels of carbon fluxes related to land use could<br />

arise from widely different socio-economic driving forces,<br />

depending on future trends in food demand and dietary<br />

pattems, agricultural productivity growth, forest practices, etc.<br />

In general, the SRES COj land-use emissions follow the same<br />

pattern as found in the literature (see Chapter 3) - initially<br />

emissions increase because of continuing deforestation in<br />

developing regions and subsequentiy they decrease following a<br />

drop in population growth and increases in agricultural<br />

productivity. The main difference between the SRES scenarios<br />

and the literature reviewed in Chapter 3 lies in the maximum<br />

emission values, which are significantly lower in the SRES<br />

scenarios. Possibly this arises because the SRES models<br />

explicitly simulate land-use change as a function of pressure on<br />

the land (itself a function of agricultural productivity), while in<br />

the literature land-use СО, emission scenarios are often based<br />

on trend extrapolation or statistical relationships (e.g. with<br />

population growth). The rapid economic development and<br />

technological advances assumed in the SRES storylines thus<br />

tend to mitigate CO, emissions from deforestation, and in<br />

some cases lead to their reversal (e.g., tuming deforested lands<br />

into carbon sinks).<br />

As suggested by Figure 5-4, no simple relation exists between<br />

the scenario families and land-use emissions. As in the case of<br />

energy-related emissions, the AI family scenarios cover the<br />

widest range of emissions and trajectories. In most cases,<br />

emissions in these scenarios decline after 2030 to zero or<br />

negative (carbon sinks) values. However, in two scenarios<br />

(AIB-IMAGE and AlB-MARlA), emissions increase later in<br />

the 2P' century, reflecting assumptions on additional land<br />

pressures. As a rale, scenarios of the A2 family follow the same<br />

convex trajectory as AI scenarios, also with two exceptions<br />

(A2-IMAGE and A2-AIM). In accordance with the<br />

sustainability emphasis of the ВI family storyline, scenarios<br />

from this family have the lowest initial emissions, which by<br />

2080 or earlier drop to zero or negative levels. The В1 family<br />

marker scenario (BI-IMAGE) has negative land-use emissions<br />

for most of the modeling period, a property directiy related to<br />

Bl's "envhonmental conservation" emphasis.

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