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Emissions Scenarios - IPCC

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Scenario Driving Forces 105<br />

3.1. Introduction<br />

Some of the major driving forces of past and future<br />

anthropogenic greenhouse gas (GHG) emissions, which<br />

include demographics, economics, resources, technology, and<br />

(non-climate) policies, are reviewed in this chapter. Economic,<br />

social, and technical systems and their interactions are highly<br />

complex and only a limited overview is provided in this<br />

chapter. The discussion of major scenario driving forces herein<br />

is structured by considering the links from demography and<br />

the economy to resource use and emissions. A frequently used<br />

approach to organize discussion of the drivers of emissions is<br />

through the so-called IPAT identity, equation (3.1).<br />

Impact = Population xAjfluence x Technology (3.1)<br />

The IPAT identity states that environmental impacts (e.g.,<br />

emissions) are the product of the level of population times<br />

affluence (income per capita, i.e. gross domestic product<br />

(GDP) divided by population) times the level of technology<br />

deployed (emissions per unit of income). The IPAT identity has<br />

been widely discussed in analyses of energy-related carbon<br />

dioxide (COj) emissions (e.g., Ogawa, 1991; Parikh et al.,<br />

1991; Nakicenovic et ai, 1993; Parikh, 1994; Alcamo et ai,<br />

1995; Gaffin and O'Neill, 1997; Gürer and Ban, 1997; O'Neill<br />

et al., 2000), in which it is often refeiTcd to as the Kaya identity<br />

(Kaya, 1990), equation (3.2).<br />

CO 2 <strong>Emissions</strong> = Population X (GDP I Population) X<br />

X (Energy/GDP) X (COJEnergy)<br />

The Kaya multiplicative identity also underlies the analysis of<br />

the emissions scenario literature (Chapter 2). It can be broken<br />

down into further subcomponents. For instance, the energy<br />

component can be decomposed into fossil and non-fossil<br />

shares, and emissions can be expressed as carbon emissions per<br />

unit of fossil energy, as shown in Figure 3-1 (Giirer and Ban,<br />

1997). A property of the multiplicative identity is that<br />

component growth rates are additive. For instance, global<br />

energy-related COj emissions since the middle of the 19*<br />

century are estimated to have increased by approximately 1.7%<br />

per year (Watson et al, 1996). This growth rate can be<br />

decomposed roughly into a 3% growth in gross world product<br />

(the sum of a 1% growth in population and a 2% growth in per<br />

capita income) minus a 1% per year decline in the energy<br />

intensity of world GDP (the third term in equation (3.2)) and a<br />

decline in the carbon intensity of primary energy (the fourth<br />

term) of 0,3% per year (Nakicenovic et al, 1993; Watson et al,<br />

1996).<br />

While the Kaya identity above can be used to organize<br />

discussion of the primary driving forces of CO2 emissions and,<br />

by extension, emissions of other GHGs, there are important<br />

caveats. Most important, the four terms on the right-hand side<br />

of equation (3.2) should be considered neither as fundamental<br />

driving forces in themselves, nor as generally independent<br />

from each other.<br />

Global analysis is often not instructive and even misleading,<br />

because of the great heterogeneity among populations with<br />

respect to GHG emissions. The ratios of per capita emissions<br />

of the world's richest countries to those of its poorest countries<br />

approach several hundred (Parikh et al, 1991; Engelman,<br />

1994). Of course, some level of aggregation is necessary. In<br />

practice, the models used to produce emissions scenarios in<br />

this report, for example, operate on the basis of 9-15 regions<br />

(see Appendix IV, Table IV-1). This level of detail isolates the<br />

most important differences, particularly with respect to<br />

industrial versus developing countries (Lutz, 1993).<br />

The spatial and temporal heterogeneity of emission growth that<br />

becomes masked in the global aggregates is shown in Figure<br />

3-1, in which the growth in energy-related COj emissions<br />

since 1970 is broken down into a number of subcomponents.<br />

For industrial countries the population growth has been modest<br />

and their emissions have evolved roughly in line with increases<br />

(or declines) in economic activity. For developing countries<br />

both population and income growth appear as important drivers<br />

of emissions. However, even in developing countries the<br />

regional heterogeneity becomes masked in the aggregate<br />

analysis (Griibler et al, 1993a).<br />

Although, at face value, the IPAT and Kaya identities suggest<br />

that COj emissions grow linearly with population increases,<br />

this depends on the real (or modeled) interactions between<br />

demographics and economic growth (see Section 3.2) as well<br />

as on those between technology, economic structure, and<br />

affluence (Section 3.3). In principle, such interactions preclude<br />

a simple linear interpretation of the role of population growth<br />

in emissions.<br />

Demographic development interacts in many ways with social<br />

and economic development. Fertility and mortality trends<br />

depend, among other things, on education, income, social<br />

norms, and health provisions. In turn, these determine the size<br />

and age composition of the population. Many of these factors<br />

combined are recognized as necessary to explain long-run<br />

productivity, economic growth, economic structure, and<br />

technological change (Barro, 1997). In turn, long-run per<br />

capita economic growth and structural change are closely<br />

linked with advances in knowledge and technological change.<br />

In fact, long-run growth accounts (e.g., Solow, 1956; Denison,<br />

1962, 1985; Maddison, 1989, 1995; Barro and Sala-I-Martin,<br />

1995) confirm that advances in knowledge and technology may<br />

be the most important reason for long-run economic growth;<br />

more important even than growth in other factors of production<br />

such as capital and labor. Abramovitz (1993) demonstrates that<br />

capital and labor productivity cannot be treated as independent<br />

from technological change. Therefore, it is not possible to treat<br />

the affluence and technology variables in IPAT as independent<br />

of each other.<br />

Pollution abatement efforts appear to increase with income,<br />

growing willingness to pay for a clean environment, and<br />

progress in the development of clean technology. Thus, as<br />

incomes rise, pollution should increase initially and later

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