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Emissions Scenarios - IPCC

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Technical Summary 25<br />

• use a variety of models to reflect methodological<br />

pluralism and uncertainty;<br />

• incorporate input from a wide range of scientific<br />

disciplines and expertise from non-academic sources<br />

through an open process;<br />

• exclude additional initiatives and policies specifically<br />

designed to reduce climate change;<br />

• cover and describe to the extent possible a range of<br />

policies that could affect climate change although they<br />

are targeted at other issues, for example, reductions in<br />

SO, emissions to limit acid rain;<br />

• cover as much as possible of the range of major<br />

underlying driving forces of emission scenarios<br />

identified in the open literature;<br />

• be transparent with input assumptions, modeling<br />

approaches, and results open to external review;<br />

• be reproducible - document data and methodology<br />

adequately enough to allow other researchers to<br />

reproduce the scenarios; and<br />

• be internally consistent - the various input assumptions<br />

and data of the scenarios are internally consistent to the<br />

extent possible.<br />

The writing team agreed that the scenario formulation process<br />

would consist of five major components:<br />

• review of existing scenarios in the literature;<br />

• analysis of their main characteristics and driving<br />

forces;<br />

• formulation of narrative "storylines" to describe<br />

alternative futures;<br />

• quantification of storylines with different modeling<br />

approaches; and<br />

• "open" review process of emissions scenarios and their<br />

assumptions<br />

As is evident from the components of the work program, there<br />

was agreement that the process be an open one with no single<br />

"official" model and no exclusive "expert teams." In 1997 the<br />

<strong>IPCC</strong> advertised in a number of relevant scientific journals and<br />

other publications to solicit wide participation in the process.<br />

To facilitate participation and improve the usefulness of the<br />

new scenarios, the SRES web site (www.sres.ciesin) was<br />

created. In addition, members of the writing team published<br />

much of the background work used for formulating SRES<br />

scenarios in the peer-reviewed literature^ and on web sites (see<br />

Appendix IV). Finally, the revised set of scenarios, the web<br />

sites, and the draft of this report have been evaluated through<br />

the <strong>IPCC</strong> expert and government review processes. This<br />

process resulted in numerous changes and revisions of the<br />

report. In particular, during the approval process of Ihe<br />

Summary for Policymakers (SPM) in March 2000 at the 5"'<br />

Session of the WG III in Katmandu changes in this SPM were<br />

agreed that necessitated some changes in the underlying<br />

document, including this Technical Summary. These changes<br />

have been implemented in agreement with the Lead Authors.<br />

5. Scenario Literature Review and Analysis<br />

The first step in the formulation of the SRES scenarios was the<br />

review and the analysis of the published literature and the<br />

development of the database with more than 400 emissions<br />

scenarios that is accessible through the web site (wwwcger.nies.go.jp/cger-e/db/ipcc.html);<br />

190 of these extend to<br />

2100 and are considered in the comparison with the SRES<br />

scenarios in the subsequent Figures. Chapters 2 and 3 give a<br />

more detailed description of the Hterature review and analysis.<br />

Figure TS-1 shows the global energy-related and industrial<br />

COj emission paths from the database as "spaghetti" curves for<br />

the period to 2100 against the background of the historical<br />

emissions from 1900 to 1990. These curves are plotted against<br />

an index on the vertical axis rather than as absolute values<br />

because of the large differences and discrepancies for the<br />

values assumed for the base year 1990. These sometimes arise<br />

from genuine differences among the scenarios (e.g., different<br />

data sources, definitions) and sometimes from different base<br />

years assumed in the analysis or from alternative calibrations.'*<br />

The differences among the scenarios in the specification of the<br />

base year illustrate the large genuine scientific and data<br />

uncertainty that surrounds emissions and their main driving<br />

forces captured in the scenarios. The literature includes<br />

scenarios with additional climate polices, which are sometimes<br />

referred to as mitigation or intervention scenarios.<br />

There are many ambiguities associated with the classification<br />

of emissions scenarios into those that include additional<br />

climate initiatives and those that do not. Many cannot be<br />

classified in this way on the basis of the information available<br />

from the database. Figure TS-1 indicates the ranges of<br />

emissions in 2100 from scenarios that apparently include<br />

additional climate initiatives (designated as "intervention"<br />

emissions range), those that do not ("non-intervention") and<br />

those that caimot be assigned to either of these two categories<br />

("non-classified"). This classification is based on the<br />

subjective evaluation of the scenarios in the database by the<br />

members of the writing team and is explained in Chapter 2.<br />

The range of the whole sample of scenarios has significant<br />

^ Alcamo and Nakicenovic, 1998; Alcamo and Swart, 1998; Anderson,<br />

1998; Gaffin, 1998; Gregory, 1998; Gregory and Rogner, 1998;<br />

Grübler, 1998; Michaelis, 1998; Monta and Lee, 1998; Nakicenovic et<br />

al, 1998; Price et al, 1998; de Vries et al., 2000; Fenhann, 2000; Jiang<br />

et al, 2000, Jung et al, 2000; Kram et al., 2000; Mori, 2000;<br />

Nakicenovic, 2000; Riahi and Roehrl, 2000; Roehrl and Riahi, 2000;<br />

Sankovski et al., 2000.<br />

The 1990 emissions from energy production and use are estimated<br />

by Marland etal. (1994) at 5.9 GtC excluding cement production. The<br />

1990 base year values in the scenarios reviewed range from 4.8<br />

(CETA/EMF14, Scenario MAGICO CO^) to 6.4 GtC<br />

(ICAM2/EMF14), see Dowlatabadi et al, 1995; Peck and Teisberg,<br />

1995.

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