Emissions Scenarios - IPCC
Emissions Scenarios - IPCC
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