Emissions Scenarios - IPCC
Emissions Scenarios - IPCC
Emissions Scenarios - IPCC
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208 An Overview of <strong>Scenarios</strong><br />
new renewable sources of energy are dependent on ongoing<br />
technological development and cost reductions.<br />
The conventional oil industry is relatively mature and the<br />
question is at what point in the 2P' century will the current<br />
reserves start to run out. However, unconventional resources<br />
are also available - shale oil, bitumen, and heavy oil. These are<br />
starting to be exploited and they will extend current<br />
conventional oil i-eserves. The gas industry is less mature and<br />
much more remains to be discovered, particularly in areas that<br />
do not currently have the infrastructure to utilize gas and<br />
consequently exploration has been unattractive. Additionally,<br />
large amounts of unconventional gas have been identified,<br />
some of which are already in commercial production (e.g., in<br />
the US). Also, huge quantities of natural gas are believed to<br />
exist as methane hydrates on the ocean floor (see Chapter 3)<br />
and it is possible that technology to exploit these will be<br />
developed at some stage. For uranium and thorium, the<br />
amount of exploration to date has been very limited, and hence<br />
the possibilities of discovering new deposits are enormous. It<br />
is likely that even a major expansion of the nuclear industry<br />
will not be limited by the amount of available uranium or<br />
thorium. With coal, the question is not one of discovery but<br />
one of economics, accessibility, and environmental<br />
acceptability.<br />
To consider future resource availability as a dynamic process,<br />
however, does not resolve the inherent uncertainties in terms of<br />
future success rates of hydrocarbon exploration, technology<br />
development for either non-conventional fossil resources or<br />
non-fossil alternatives, or future energy prices. Therefore, these<br />
uncertainties are explored by adopting different scenario<br />
assumptions that range from low to (very) high resource<br />
availability (see Table 4-4), consistent with the interpretation of<br />
the various scenario storylines presented in Section 4.3. This<br />
scenario approach is especially important given that<br />
hydrocarbon occurrences are the largest storage of carbon.<br />
<strong>IPCC</strong> WGII SAR (Watson et al., 1996) estimates the size of the<br />
total carbon "pool" in the form of hydrocarbon occurrences to<br />
be up to 25,000 GtC. How much of this eventually could<br />
become atmospheric emissions is at present unknown, and<br />
depends on the future evolution of technology, prices, and<br />
other incentives for future hydrocarbon use and their<br />
alternatives.<br />
Given that long-term emission scenarios invariably rely on<br />
quantification by formal models, an important distinction<br />
needs to be made between assumptions concerning the ultimate<br />
resource base and projected actual resource use. Typically,<br />
assumptions on the ultimate resource base enter models as<br />
exogenously specified constraints - cumulative future<br />
production simply cannot exceed values specified as the<br />
resource base. Actual resource use, or what is frequently<br />
termed the "call on resources" conversely depends on<br />
numerous other factors represented in models, such as:<br />
• Future price levels (either assumed as exogenous inputs<br />
or determined endogenously in the model).<br />
• Assumptions on future technology improvements that<br />
either enable unconventional hydrocarbons to be<br />
"mined" economically or, conversely, that draw on nonfossil<br />
alternatives and/or non-climate environmental<br />
and social constraints (e.g., limits on particulates and<br />
sulfur emissions or on land degradation and mining<br />
accidents).<br />
Their complex interplay results in scenarios of future<br />
cumulative resource use being the most appropriate indicator,<br />
as opposed to exogenously pre-specified resource-base<br />
constraints, especially in view of the multi-model approach<br />
adopted to develop the SRES scenarios. Table 4-10 and Figures<br />
4-8 to 4-10 summarize the results for the four SRES marker<br />
scenarios and of the ensemble of SRES scenarios for their<br />
respective scenario families and scenario groups (in the case of<br />
the Al scenario family). It is evident that, in the absence of<br />
climate policies, none of the SRES scenarios depicts a<br />
premature end to the fossil-fuel age. Invariably, cumulative<br />
fossil-fuel use to 2050 (not to mention 2100) exceeds the<br />
quantities of fossil fuels extiacted since the onset of the<br />
Industrial Revolution, even though the "call on" fossil<br />
resources differs significantiy across the four marker scenarios.<br />
This increase is higher in the scenarios that explore a wider<br />
domain of uncertainty on future fossil-resource availability.<br />
For non-fossil resources, like uranium and renewable energies,<br />
future resource potentials are primarily a function of the<br />
assumed rates of technological change, energy prices, and<br />
other factors such as safety and risk considerations for nuclear<br />
power generation. Generally, absolute resource constraints do<br />
not become binding in the marker scenarios or other scenarios.<br />
The contribution of these resources is substantially below the<br />
physical flows identified in Section 3.4, and therefore resuhs<br />
mainly from scenario-specific assumptions concerning<br />
technology availability, performance, and costs. These are<br />
summarized in Section 4.4.7.<br />
4.4.6.1. Al <strong>Scenarios</strong><br />
Energy resources are taken to be plentiful by assuming a large<br />
future availability of coal, unconventional oil, and gas as well<br />
as high levels of improvement in the efficiency of energy<br />
exploitation technologies, energy conversion technologies, and<br />
transport technologies. The grades of energy resources used in<br />
the model differ on the basis of extraction costs. When<br />
combined witl; the level of improvement in efficiency of<br />
exploitation technology (expressed as the rate of improvement<br />
in marginal production costs), the graded costs of energyresource<br />
exploitation determine the energy production costs<br />
(prices) and hence the ultimate resource extraction quantities.<br />
For AI, large amounts of unconventional oil and natural gas<br />
availability were assumed. Cumulative (1990 to 2100)<br />
extraction of oil ranges between 15 and 30 ZJ in the Al<br />
scenarios (AIB marker, 17 ZJ); for gas the range is between 23<br />
and 48 ZJ (AIB marker, 36 ZJ) and for coal the range is<br />
between 8 and 50 ZJ (AIB marker, 12 ZJ). Resource<br />
availability and reliance uncertainties are also explored through