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Emissions Scenarios - IPCC

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Emission <strong>Scenarios</strong> 291<br />

Box 5-5: Gridding of Emission Data<br />

The cHmate effects of SO^ are intrinsically regional and emissions on a latitude-longitude grid are required as input to climate<br />

models. <strong>Emissions</strong> of SOj were first standardized for four world regions as described above. Then, emissions from the marker<br />

scenarios for six regions (OECD90, REF, Centrally Planned Asia, Rest of Asia, Latin America, and Africa/Middle East, scaled<br />

to match the standardized emissions) were used for gridding purposes. For the Aimex П countries, a value of 23 MtS was taken<br />

for 1990 emissions, a figure derived from a compilafion of country-level emissions inventories (Smith et al., 2000).<br />

These emissions were mapped to a global 1° x 1° emissions grid. For each region, the pattern of total SO^ emissions from the<br />

EDGAR database (Olivier et ai, 1996) was scaled by the total emissions for that region and a time period. <strong>Emissions</strong> for<br />

OECD90 countries were first scaled individually to their country-specific values. The value of 3 MtS was added to reflect<br />

intemational shipping, with the pattern and magnitude of these emissions held constant.<br />

<strong>Emissions</strong> of other short-lived gases (CO, N0^^, NMVOCs, and CH^) also needed to be mapped to a global grid for use in<br />

atmospheric chemistry models. The approach taken was essentially the same, with the EDGAR database used to establish the<br />

spatial pattern. Standardization and subsequent gridding were carried out at the level of the origmal four world regions, and no<br />

specific adjustments were made for intemational shipping.<br />

In "high income regions" (OECD90, REF) sulfur emissions<br />

have already passed their peaks and are actually declining at<br />

present. This trend is expected to continue in all the markers,<br />

except A2 in which an increased use of coal "counters" a<br />

decline in specific emissions in OECD90 (Figure 5-20).<br />

<strong>Emissions</strong> in ASIA grow in all the markers by 2020, and then<br />

decline by 2050, and further decline by 2100. The most<br />

dramatic decline is registered in the AIB marker; this is related<br />

to its aggressive assumptions on the introduction of low-sulfur<br />

technologies and fuel switching in the ASIA region (see Box 5-<br />

3 for more details). Unlike ASIA, the ALM region sees<br />

increases in emissions in all four markers from 2020 to 2050,<br />

because of the somewhat "mixed" nature of this region, which<br />

combines countries with substantially different affluence levels<br />

and development trends. However, by 2100, when low-sulfur<br />

technology becomes widely available everywhere, emissions in<br />

the ALM decline in all markers (Figure 5-20).<br />

5.6.2. Gridded Sulfur <strong>Emissions</strong><br />

As discussed above, global sulfur emissions eventually decline<br />

in all SRES scenario families and associated groups. In<br />

addition, the regional distribution of emissions changes<br />

drastically over time. While in previous decades major sulfur<br />

emitters were located primarily in industrialized regions of the<br />

world, presently emissions for these sources are declining<br />

because of the introduction of cleaner fuels and the conversion<br />

to low-sulfur technologies to comply with environmental<br />

regulations. In the majority of SRES scenarios, this trend is<br />

expected to continue. Meanwhile, less-developed regions are<br />

anticipated to experience strong economic growth associated<br />

with an increased demand for energy. Especially in the short<br />

term, fossil fuels are likely to satisfy the major share of this<br />

new demand, which may lead to a steep initial growth in sulfur<br />

emissions. As mentioned eariier (see Section 5.5.2), at some<br />

point in time sulfur emissions will be controlled in all the<br />

scenarios and, together with shifts to essentially sulfur-free<br />

energy resources, they will decrease in the developing regions<br />

as they are decreasing now in the industrialized world. As a<br />

consequence of these complex dynamics, different countries<br />

and regions are bound to experience very different levels of<br />

sulfur emissions over the 2P' century. To illustrate this. Figure<br />

5-21 shows gridded sulfur emissions in 1990 and 2050 in the<br />

AIB marker (see Box 5-5).<br />

References:<br />

AFEAS (Altemative Fluorocarbons Environmental Acceptability Study),<br />

1998: Production, Sales and Atmospheric Release of Fluorocarbons<br />

Through<br />

1997. AFEAS, Washington, DC.<br />

Akimoto, H., and H. Narita, 1994:<br />

Distribution of SO,, N0^, and CO^<br />

emissions from fuel combustion and industrial activities in Asia with l^xl"<br />

resolution. Atmospheric Environment, 28(2), 213-225.<br />

Alcamo, J., A. Bouwinan, J. Edmonds, A. Grübler, T. Morita, and A.<br />

Sugandhy, 1995: An evaluation of the <strong>IPCC</strong> IS92 emission scenario.s. In<br />

Climate Change 1994, Radiative Forcing of Climate Change and An<br />

Evaluation of the I P C C IS92 Emission <strong>Scenarios</strong>, J.T. Houghton, L.G.<br />

Meira Filho, J. Bruce, Hoesung Lee, B.A. Callander, E. Haites, N. HaiTis<br />

and K. Maskell (eds.), Cambridge University Press, Cambridge, pp. 233-<br />

304.<br />

Alcamo, J., J. Onigkeit, and F. Kaspar, 1997; The Pollutant Burden Approach<br />

for Computing Global and Regional <strong>Emissions</strong> of Sidfur Dioxide. Center<br />

for Environmental Systems Research, University of Kassel, Kassel,<br />

Germany.<br />

Amann, M., I. Bertok, J. Cofala, F. Gyarfas, C. Heyes, Z. Klimont, M.<br />

Makowski. W. Schoepp, and S. Shlbayev, 1996: Cost-Effective Control of<br />

Acidification and Ground-Level Oro/i

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