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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

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