Emissions Scenarios - IPCC
Emissions Scenarios - IPCC
Emissions Scenarios - IPCC
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132 Scenario Driving Forces<br />
electricity generated by fossil fuels. Conversely, if biomass use<br />
was previously on an unsustainable basis, the shift toward<br />
commercial fuels can lower carbon intensities. The trend<br />
toward replacement of biomass fuels by commercial fuels is<br />
expected to continue in developing countries (lEA, 1995).<br />
In addition to the energy use in buildings, Tiwari and Parikh<br />
(1995) drew attention to energy use for buildings construction,<br />
which accounts for 17% of India's carbon emissions in tenns<br />
of embodied energy in steel, cement, glass, bricks, etc.<br />
Typically, this embodied buildings energy is accounted for as<br />
industrial energy use in energy statistics. Tiwari and Parikh<br />
(1995) found that in India alternative construction methods<br />
could save 23% of energy use at 0.03% increase in costs.<br />
3.4.2.4. Transport<br />
The transport sector consumed slightly over 63 EJ, or about<br />
20% of global primary energy, in 1990. Transport sector<br />
primary energy use grew at a relatively rapid average annual<br />
rate of 2.8% between 1971 and 1990, slowing to 1.7% per year<br />
between 1990 and ¡995. Industrialized countries clearly<br />
dominate energy consumption in this sector, using 62% of the<br />
world's transport energy in 1990, followed by REF (16%),<br />
ALM (12%), and ASIA (10%) regions. The most rapid growth<br />
was seen in the ASIA countries (5.9% per year) and the ALM<br />
region (4.6% per year). Transport energy use dropped<br />
dramatically in the REF region after 1990; by 1995 this region<br />
only consumed 11% of global transport energy use. Growth in<br />
transpoit primary energy use also declined slightly in the IND<br />
region, dropping from an average of 2.2% per year between<br />
1971 and 1990 to 1.9% per year between 1990 and 1995. High<br />
growth continued in the ASIA and ALM regions, with the<br />
ASIA countries increasing to an average of 7.6% per year<br />
between 1990 and 1995 (BR 1997; lEA, 1997a; lEA, 1997b).<br />
Influences on GHG emissions from the transport sector are<br />
often divided into those that affect activity levels (travel and<br />
freight movements) and those that affect technology (energy<br />
efficiency, carbon intensity of fuel, emission factors for nitrous<br />
oxide (NjO), etc.). The various driving forces and their effects<br />
are reviewed in detail in the <strong>IPCC</strong> Working Group II (WGII)<br />
Second Assessment Report (SAR) (Michaelis et al., 1996).<br />
In aggregate, transport patterns are closely related to economic<br />
activity, infrastructure, settlement pattems, and prices of fuels<br />
and vehicles. They are also related to communication links. At<br />
the household level, travel is affected by transport costs,<br />
income, household size, local settlement patterns, the<br />
occupation of the head of the household, household make-up,<br />
and location (Jansson, 1989; Hensher et al., 1990; Walls et al.,<br />
1993). People in higher-skilled occupations that require higher<br />
levels of education are more price- and income-responsive in<br />
their transport energy demand than people in lower-skilled<br />
occupations (Greening and Jeng, 1994; Greening et al., 1994).<br />
Urban layout both affects and is affected by the predominant<br />
transport systems. It is also strongly influenced by other factors<br />
such as people's preference for living in low-density areas,<br />
close to parks or other green spaces, away from industry, and<br />
close to schools and other services. Travel pattems may be<br />
influenced by many factors, including the size of the<br />
settlements, proximity to other settlements, location of<br />
workplaces, provision of local facilities, and car ownership. A<br />
survey of cities around the world (Newman and Kenworthy,<br />
1990) found that population density strongly and inversely<br />
correlates with transport energy use.<br />
Many studies have examined the response of car travel and<br />
gasoline demand to gasoline price, and are reviewed, for<br />
example, in Michaelis (1996) and Michaelis et al. (1996). Such<br />
studies typically find a measurable reduction in fuel demand,<br />
distance traveled, car sales, and energy intensity in response to<br />
fuel price increases. Studies of freight transport found<br />
relatively small short-term impacts of diesel price increases,<br />
and often produced results that were inconclusive or<br />
statistically insignificant. Over the longer term, price<br />
responsiveness is generally assumed to be larger because of<br />
possible technology responses.<br />
An important influence on future travel may be the<br />
development of telecommunication technologies. In some<br />
instances, improved communication can substitute for travel<br />
as people can work at home or shop via the intemet. In others,<br />
communication can help to increase travel by enabling<br />
friendships and working relationships to develop over long<br />
distances, and by permitting people to stay in touch with their<br />
homes and offices while traveling. To the extent that<br />
improvements in telecommunication technology stimulate the<br />
economy, they are likely to result in increased freight<br />
transport.<br />
Energy intensity in the transport sector is measured as energy<br />
used per passenger-km for passenger transport and per ton-km<br />
for freight transport. Transport energy projections typically<br />
incorporate a reduction in fleet energy intensity in the range 0.5<br />
to 2% per year (Grübler et al, 1993b; lEA, 1993; Walsh,<br />
1993). On-road energy intensity (fuel consumption per<br />
kilometer driven) of Hght-duty passenger vehicles in North<br />
America fell by nearly 2% per year between 1970 and 1990, to<br />
about 13 to 14 liters per 100 kilometers, but it is now stationary<br />
or rising. In other industrialized countries, changes in on-road<br />
fuel consumption from 1970 to the present were quite small.<br />
The average on-road energy intensity in North America was<br />
85% higher than that in Europe in 1970, but only 25 to 30%<br />
higher by the mid-1990s (Schipper, 1996).<br />
In some countries, such as Italy and France, where fleet<br />
average energy intensity has fallen during the past 20 years, the<br />
energy intensity of car travel (MJ/passenger-km) has increased<br />
as a result of declining car occupancy and the increasing use of<br />
more efficient diesel vehicles (Schipper et al, 1993). However,<br />
conversion to diesel has been encouraged by low duties on<br />
diesel fuel relative to those on gasoline. The lower costs of<br />
driving diesel vehicles may have acted as a significant stimulus<br />
to travel by diesel car owners, and so offset much of the energy