Car travel: Asia cannot follow Australia's path. Part 2
32
Car travel: Asia
cannot follow
Australia’s path
P. Moriarty
Refereed Paper
This paper has been critically reviewed by at least
two recognised experts in the field.
Originally submitted: November 1999
Vol 9 No 2 June 2000 Road & Transport Research
Abstract
This paper analyses the future of car ownership and
use in Asia. Because urban residents have higher
than average incomes, car ownership is much higher
in cities than in rural areas, athough still low by
Australian standards. Yet Asia’s rapidly growing
and densely populated cities already suffer serious
traffic congestion, accidents, and air pollution, which
higher car ownership can only exacerbate. It does
not seem possible to improve traffic speeds by road
construction on the scale needed for car-dominated
transport systems. Asia’s low oil reserves, lack of
suitable alternative fuels, and its rising total
greenhouse gas emissions cast further doubt on a
car-oriented future. A more suitable transport system
for large, congested cities would stress heavy-rail,
which is not only far more land-use and fuel efficient
than car travel, but also will often be faster. For less
congested cities, both large and small, busway
systems, which are also both land-use and fuel
efficient, show promise as a cost-effective solution.
Also needed are urban road pricing, and
encouragement of the already high levels of nonmotorised travel in both urban and rural areas.
Car travel: Asia cannot follow Australia's path. Part 2
33
In 1996, the world motor vehicle fleet numbered nearly
700 million, including over 500 million cars. Only
about 75 million of these cars, or 15%, were in Asia
(World Bank 1998). (In this paper, Asia includes all
those countries bounded by (and including) Pakistan
to the west and China to the north, or all Asia except for
the Middle-East and the republics of the former USSR.)
At first glance, the future potential for greatly increased
car ownership in Asia appears enormous. Asia so
defined in 1996 had 3224 million people, or 55% of the
world total (World Bank 1999). Economic growth
rates for many countries in this region have been high,
with the largest (China and India) little affected by the
1997 Asian economic crisis. Economic growth in any
case had picked up in the affected countries by 1999
(Organisation for Economic Cooperation and
Development (OECD) 1999).
A strong case can be made for high future growth
rates in Asian car travel. One method for projecting
future car ownership is to make use of the experience
of more developed countries as a ‘template’ for car
ownership in less developed countries. Ballew and
Schnorbus (1993), for example, used South Korea’s
experience of growth in income and car ownership
as a model for China. On this basis they projected
China’s car population to reach 36 million in the
year 2010, noting that in South Korea “vehicle sales
and all consumer durables exploded once per capita
income reached approximately $3500 a year”.
Similarly, Dargay and Gately (1997) forecast by 2015
nearly 60 million cars in China and over 450 cars per
1000 population in Taiwan and South Korea. More
generally, Japan has been implicitly used as a model
for Asian industrialising countries, and in 1996
Japanese car ownership reached 374 per 1000
population (World Bank 1998). Finally, there is the
example of the car-oriented Western countries,
including neighbouring Australia, with their even
higher levels of car ownership.
Many countries in Asia are promoting domestic car
industries (Taylor 1997), which has contributed to
the recent rapid growth in local car ownership
(Allport 1996). In former Asian centrally planned
economies, private ownership of cars was
discouraged in the past, and in some cases prohibited.
Today, these constraints have been largely lifted. In
China, for example, auto manufacturing has been
designated as one of the five ‘pillar’ industries for
development in the early twenty-first century, with
the long-term goal of a car for 270 million (or 90%) of
Chinese families (Smil 1997). Calder (1996) similarly
argues that for China ‘a long-range projection of 300
million cars on the road is not unreasonable’.
Table 1
Cars per 1000 population in Australia and various Asian countries, 1960–95
Country
Australia
China
India
Indonesia
Hong Kong
Japan
Malaysia
Pakistan
Singapore
South Korea
Taiwan
Thailand
Year
1960
1970
1980
1990
1995
196
0
1
1
11
5
13
2
40
1
1
2
307
0
1
2
23
85
26
2
60
2
3
5
401
0
1
4
36
203
62
2
65
7
41
9
437
1
3
6
37
283
69
4
105
49
114
15
485
3
4
11
55
374
131
5
120
151
193
28
Sources: UN 1997; World Bank 1998.
Vol 9 No 2 June 2000 Road & Transport Research
Car travel: Asia cannot follow Australia's path. Part 2
34
Despite this high-growth picture for Asian car travel,
this paper argues that the rapid growth in car
ownership and use observed in recent years cannot
continue for long. The following sections first analyse
the various factors that presently constrain car
ownership and use, then examine probable future
constraints. The last major section suggests ways in
which the transport systems in Asian countries could
be adjusted to meet these serious constraints.
HISTORICAL PATTERNS OF CAR
OWNERSHIP IN ASIA
This section considers only the spread of car
ownership in Asia, as data on car usage, although
preferable, is only available over the period for
Japan. In 1960, the world’s cars totalled only about
98 million. The countries of western Europe, the
United States (US), Canada, and Australasia together
owned 92% of this total, with nearly 63% in the US
alone. Asia’s share, however, was little more than
1% (United Nations (UN) 1997). Table 1 shows car
ownership data for Australia and a number of Asian
countries, including both the largest, and the most
economically advanced. Ownership remained low
in all countries except Japan until 1980. Since then,
and particularly since 1990, car ownership has passed
100 per 1000 population in several countries, and at
374 Japan is not far below the average West European
figure of 434 cars per 1000 population (Euromonitor
1998). In poor countries, such as most of Asia in the
1960s, low per capita incomes inhibited car ownership
and use, just as it still does today in the low income
countries of tropical Africa, for example.
Low average per capita incomes can explain the low
rates of car ownership in only a few Asian countries
today. Existing car ownership in the region is still
low when compared with income levels, as Table 2
demonstrates for the most developed Asian
economies. (The Gross National Product (GNP)
values are expressed in Purchase Parity Prices (PPP),
as these better compare actual transport purchasing
power for different countries than do GNP values
based on exchange rates.) ‘Car intensities’, defined
here as cars/US$million GNP, are low compared
with Australia, whose value is typical of the OECD
(World Bank 1998). On a vehicle-kilometre basis,
intensities are even lower, since cars appear to be
driven much less per year than in Australia
(Euromonitor 1998).
The last column in Table 2 shows that per kilometre
of road length, vehicle numbers (excluding twowheelers) are far higher in Asian countries than in
Australia. Even these high numbers underestimate
levels of road use in Asia. Ownership of motorcycles
in the poorer countries is usually several times higher
than that for cars, while in Japan, Malaysia, and
Thailand, it exceeds 100, and in Taiwan, 400 per 1000
population. For Australia the figure is only 16 per
1000 population (World Bank 1998). In addition,
roads must also cater for heavy bicycle traffic, and
even animal-drawn vehicles (Replogle 1992). Vehicle
numbers have also risen much more rapidly than
road space provision in many Asian countries. For
example, from 1980 to 1996, road vehicles per
kilometre (excluding two-wheelers), rose from 11 to
106 in South Korea, and from 13 to 97 in Thailand
Table 2
Transport parameters, Australia and various Asian countries, 1996
Country
Australia
Hong Kong
Japan
Malaysia
Singapore
South Korea
Thailand
GNP/capita
(1996 US$ PPP)
Cars per
$m. GNP
19 870
24 260
23 420
10 390
26 190
13 080
6 700
24.4
2.3
16.0
12.6
4.5
11.5
4.2
Source: World Bank 1998.
Vol 9 No 2 June 2000 Road & Transport Research
Vehicles/km.
of road
12
276
60
33
168
106
97
Car travel: Asia cannot follow Australia's path. Part 2
35
(World Bank 1998). Lack of road space is thus a
probable contributory factor for Asia’s low car
intensity.
URBAN CONGESTION IN ASIAN
COUNTRIES
The previous section dealt with car ownership trends
at the national level, whereas this section will examine
the situation in Asian cities. The data in Table 2
suggest considerable unmet demand for cars in Asia,
and this is especially true for its congested cities (Birk
and Reilly-Roe 1991). Table 2 shows that car intensity
is very low for the affluent city states of Singapore
and Hong Kong. Further, Tokyo and Osaka have
much lower car intensities than Japan overall, whereas
in Australia’s largestcities, Sydney and Melbourne,
car intensities are similar to the overall national
average (Australian Bureau of Statistics (ABS) 1997;
Japan Statistical Association 1998).
Although car ownership and usage are still low,
large Asian cities are already among the most
congested in the world (Kubota 1996). Cities in
developing Asian countries usually have much
higher per capita incomes than do rural areas (e.g.
State Statistical Bureau (1998), for Chinese data, and
National Statistical Office (1998) for Thai data), which
help explain why urban population growth is
expected to be so rapid. Because of these higher
incomes, car ownership also tends to be much higher.
In Thailand, for example, 65% of all registered cars
operate in the Bangkok metropolis, which has only
9.3% of the population (National Statistical Office
1998). In other words, demand for cars will be
highest in Asian cities, which unfortunately are
where congestion and air pollution are worst (World
Resources Institute (WRI) 1996).
In most developing Asian countries, city size is set to
grow, since the degree of urbanisation, although
presently low, is projected to increase rapidly as
industrialisation and economic growth occur (World
Bank 1998). For example, the urban population of
China is projected to increase from its 1995 level of
30% to 51% by 2020, representing an increase from
369 million to 756 million urban residents. India’s
urban population is expected to reach 547 million,
and Indonesia’s 151 million by 2020 (UN 1999). This
overall urban expansion will be reflected in largecity growth. Already, Asia contains 13 of the world’s
25 largest cities, and these are among the fastest-
growing (WRI 1996). Projected populations of the
largest cities in Asia in 2015 show five (Tokyo,
Bombay, Shanghai, Jakarta and Karachi) in the 20–
30 million range and a further ten cities with 10–20
million (World Bank 1998).
Asian cities are also far denser than those in Australia.
Newman and Kenworthy (1999) give an average
value for population density in six large Australian
cities as 1220/km2, compared with 16 190/km2 for
nine large Asian cities. Further, in Australia,
suburbanisation has reduced urban densities: in
1960, about 8% of the total population lived at urban
densities of greater than 4000/km2, but by 1996,
only some 2% did so (ABS 1997). In Japan, by contrast,
the proportion of the population living in ‘densely
inhabited districts’ (4000/km2 or higher) rose from
48% to 65% over the years 1965–95 (Japan Statistical
Association 1998). Future prospects for significantly
decreasing urban densities in the cities of developing
Asia do not look promising either. Gardner (1997) of
the Worldwatch Institute argues that because of the
need to preserve cropland, most Asian countries
will not be able to release much land for city growth.
In a decade or two, he foresees insufficient grain on
the world market for Asia to import. The World
Bank (1999), on the other hand, feel that this
assessment is too pessimistic. But the possibility
remains that future urban population growth in
most Asian countries will need to be at densities
similar to today’s, with serious consequences for
urban road congestion and air pollution if vehicle
numbers continue to grow.
The suburbanisation that occurred in Australian
cities has been successful overall in preventing
deterioration of urban traffic speeds, despite
increasing vehicle numbers, as evidenced by the
data for 1960–1990 in Newman and Kenworthy
(1989, 1999). More indirect evidence is the converging
fuel efficiencies of urban and non-urban car operation
(Apelbaum Consulting Group 1997). In contrast, in
many Asian cities, peak-hour speeds fell during the
1980s (Bose 1996, Kubota 1996; WRI 1996). The
peak-hour average for Asian cities is now estimated
to be 16 km/h, with much lower speeds in Bangkok
(Kubota 1996; World Bank 1998). Evidently, cars in
many Asian cities spend much of their time stationary
in traffic jams; in Bangkok, the equivalent of 44 days
per year! (World Bank 1998). This congestion, along
with high-emission vehicle fleets (both private and
public), already causes very serious air pollution.
Vol 9 No 2 June 2000 Road & Transport Research
Car travel: Asia cannot follow Australia's path. Part 2
36
Beijing, for example, has only 10% of Los Angeles’
automobiles, but its aggregate automotive emission
levels are similar (World Bank 1997). Even if, as is
likely, emissions per vehicle-kilometre are lowered,
rising vehicle numbers could mean that no net
improvement occurs.
Nor does it seem possible to improve speeds by
building new roads, even if the land could be made
available. Given the substantial latent demand for
urban car ownership and travel, it is very likely that
any attempt to increase road space, never an easy
task in densely populated cities (Xin 1996), will
merely result in higher car ownership and use, with
no improvement in traffic speeds. In Bangkok, for
example, it was estimated in 1991 that the city would
need to invest US$100 billion just to maintain present
(serious) levels of traffic congestion (Birk and ReillyRoe 1991). The UN (1999) and Allport (1996) have
also recognised that simply providing more road
space is not a solution, and that traffic restraint
measures are needed.
PROBABLE FUTURE CONSTRAINTS
In 1999, global oil consumption averaged 75.2 million
barrels per day, or 27.4 billion barrels of oil per
annum, with growth in consumption having already
resumed in Asia (ABARE 1999). Proven reserves in
Asia are only about 5% of the world total, with
reserves to production ratio well below the world
average (US Department of Energy 1998). Reserves
of non-conventional oil are even smaller, at around
2% (Attanasi and Root 1995). There are presently
several minor Asian oil exporters, but Asia overall is
a large net importer. China’s oil imports alone are
projected to rise to seven million barrels/day by
2015 (Far Eastern Economic Review 1997). The global
demand for conventional oil is forecast to outstrip
supply at present prices after 2010 (Campbell and
LaHerrere 1998; International Energy Agency (IEA)
1998). Asian countries will likely become increasingly
vulnerable to supply disruptions and price increases
(Calder 1996).
Depletion of conventional oil is not the only possible
future constraint. The transport sector worldwide is
an important producer of heat-trapping greenhouse
gases (GHGs). While per capita emissions of carbon
dioxide (CO2) are still low, a large and increasing
share of total emissions comes from Asian countries.
For example, even with dramatic improvements in
energy efficiency and promotion of nuclear and
Vol 9 No 2 June 2000 Road & Transport Research
hydro electricity, China’s present CO2 emissions of
2.6 billion tonnes are projected to grow by 2025 to
11.7 billion tonnes, or half the present world total.
Even then per capita emissions in China would still
be much less than the current US figure (Drennen
and Erickson 1998). Evidently, if global emissions
are to be reduced, the industrialising Asian countries
will need to cut emissions as well as the OECD
countries (World Bank 1999). Finally, increasing
reliance on non-conventional oil will worsen CO2
emissions, because of higher energy costs per barrel
delivered to market.
Two possibilities for overcoming these constraints
are alternative fuel use and more fuel-efficient
vehicles. Alternative carbon-based fossil fuels will
be of little use for GHG reductions. Similar problems
face Asian options for ethanol from biomass, given
that the region is already a major net food importer
(World Bank 1998). Improving fuel efficiency appears
to offer more promise, as the potential is large.
However, actual progress has been slow, probably
because of declining real oil prices. Indeed, for the
Japanese car fleet, energy/passenger-kilometre is
now rising because of declining vehicle occupancy
rates (IEA 1997; Japan Statistical Association 1998).
Even if, very optimistically, new car fuel efficiency
could be radically improved in industrialising Asian
countries, projected growth in vehicle numbers
would soon swamp any fuel efficiency gains.
Australia has better prospects for alternative fuels
(especially natural gas) than Asia, and traffic growth
has slowed. Even so, it is possible that deep cuts in
greenhouse gas emissions, if needed, would also
necessitate car travel reductions here.
POLICY IMPLICATIONS
The previous sections have highlighted several
constraints on future Asian car travel that call for
policy responses by transport planners. Urban
congestion and pollution can only be exacerbated if
both car ownership and population continue to rise.
It does not seem possible, therefore, for most Asian
countries to adopt the car-oriented transport system
of Australia. Different approaches to transport
planning, particularly in large congested cities, are
urgently needed. Some general ideas for a less caroriented direction are discussed in this section.
The preceding sections have implicitly spelled out
the characteristics required for Asian transport
systems to meet the inevitable growth in travel in the
Car travel: Asia cannot follow Australia's path. Part 2
37
twenty-first century. They must be efficient in their
use of oil, and keep GHG emissions to a minimum.
Particularly for large cities, they must be very landuse efficient, needing only small areas of land
(including land for parking) to accommodate the
movement of high volumes of travellers per hour.
They also should minimise exhaust pollutants, a
major problem in Asian cities. Vehicular transport
should restrict neither the safety nor the freedom of
movement of non-motorised travel. And, of course,
the overall transport system should aim for high
traveller convenience and low costs.
Allport (1996) argues that controlling traffic
congestion is the core objective in large, heavily
congested Asian cities. In these cities, a vehicular
solution that meets many of the above criteria is
electric fixed-rail transport with its own right of
way. Electric rail is far more land-use efficient than
car travel. With practical minimum headways of 90–
120 seconds, 30–40 trains per hour can be
accommodated on one track. For eight-car trains,
and 100 seats per car, a seated passenger volume of
32 000/hour can be obtained. With passengers
standing, much higher volumes are possible. Lines
in Moscow, New York and Tokyo carry 50 000 or
more, while Hong Kong’s Mass Transit Railway
attains up to 80 000 passengers per hour per line
(Black 1995; White 1995). In contrast, a single lane on
a multi-lane freeway can only carry about 2300 cars
or about 4000 persons per hour, even under ideal
conditions. As traffic density (that is, vehicles per
kilometre of road lane) increases past an optimum
value, the carrying capacity decreases. On ordinary
arterial roads, with cross-traffic, the figure will be
even lower (Wright 1996). In some Asian cities, the
presence of large numbers of bicycles, and even
animal-drawn vehicles, will further reduce motorised
traffic volumes.
An important consequence of the low and often
deteriorating traffic speeds in Asian cities is that
heavy-rail transport will often be faster, even at offpeak times. These shorter travel times for rail
(together with zero time and money parking costs)
can go a long way towards overcoming the inherent
advantages of private car travel, such as privacy,
weather protection, and door-to-door travel.
Although congestion on heavy-rail services decreases
travel speeds somewhat, because of the need for
greater stopping times at stations, it greatly enhances
land-use efficiency, as measured by passengerkilometre per line per hour, as well as energy
efficiency. For vehicular road travel, on the other
hand, congestion not only greatly increases travel
times, but also actually reduces both landuse and
fuel efficiency, and increases air pollution. Under
the congested conditions typical of large Asian cities,
heavy-rail is at least an order of magnitude more
land-use efficient than private car travel. It should be
no surprise that some of the world’s busiest systems
are already to be found in large Asian cities such as
Tokyo and Hong Kong. Other large Asian cities, for
example, Delhi (Bose 1996), may need to follow their
example. Such rail systems will also have much
lower transport oil use and greenhouse gas emissions
than car-based systems, and no air pollution at the
point of use.
For less congested cities, or the more lightly-trafficked
routes in large, generally congested cities, busway
systems will probably be preferable to heavy rail
(Gardner 1992; Allport 1996). To achieve high
passenger volumes and reasonable travel speeds,
busways need dedicated lanes physically separated
from general traffic lanes, and traffic signal priority.
On the best systems, volumes of 20 000 passengers
per hour per direction have been measured, although
speed and capacity fall off closer to the city centre.
The costs are far lower than that for heavy rail
systems (Gardner 1992).
Improved road user charging will also be needed in
many Asian cities, following the example of
Singapore (Lewis 1994). In the industrialising Asian
countries, where car ownership is low, equity
considerations will be a minor problem compared
with Australia, where car ownership is high, even
among low-income households. Road user charging
in congested cities can, by raising perceived motoring
costs, optimise traffic volumes and reduce both fuel
consumption and air pollution, as well as raising
revenue.
Planners also need to recognise non-motorised
transport as an important and permanent feature of
Asian travel (Thomas et al. 1992; Goodland 1994),
one that can complement public transport. These
cheap modes of transport are still heavily used in
Asia, in both rich and poor countries. China, for
example, reportedly has over 300 million bicycles
(Replogle 1992). Like heavy-rail, non-motorised
modes have high land-use efficiency, as well as no
oil use and no local or global emissions. Traffic safety
is their biggest problem. Most traffic fatalities in
industrialising countries are not vehicle occupants,
Vol 9 No 2 June 2000 Road & Transport Research
Car travel: Asia cannot follow Australia's path. Part 2
38
but rather pedestrians, pedal cyclists and motor
cyclists, especially in urban areas (Moriarty and
Honnery 1999). Although high fatality rates have
not usually been seen as a constraint on growing
vehicle use, they do suggest the need for urgent
transport policy changes. China and India are among
the world leaders in absolute numbers of traffic
fatalities (Navin, Bergan and Jinsong 1994). Further,
Navin et al. (1994) project fatalities in China to rise to
180 000 before peaking, if vehicle ownership
continues to rise. Xin (1996) argues that constraints
on urban vehicle ownership will be required, if
vehicular traffic is not to endanger non-motorised
travel in densely populated cities. (Allport (1996)
likewise argues for car restraint, but for controlling
congestion.) Probably also needed are dramatic cuts
in permissible vehicle speeds for remaining vehicular
traffic, in order to reduce the frequency and severity
of impacts with pedestrians and cyclists.
Finally, for those living in the rural areas of most
Asian nations, low incomes preclude significant
increases in car ownership, even if traffic congestion
is much less of a constraint than in cities. Rising oil
prices and carbon taxes , if levied, will make it even
more difficult in the future. Rural residents will have
to continue to meet their travel needs much as they
do today, mainly by a combination of non-motorised
modes, and for longer trips, bus and rail travel, if
available.
CONCLUSIONS
Two conditions must be met for high car ownership
and use in any country. First, most individual
households must have sufficient disposable income
to own and operate cars. Second, there must be an
adequate infrastructure to support the resulting high
levels of traffic. Asian car travel would be much
higher if both incomes and population were more
evenly distributed spatially, as is the case for
Malaysia. But both income and population
distribution seem set to become even more spatially
skewed in the future. In the cities of developing
Asian countries, the combination of rapid urban
population growth and much higher than average
incomes will ensure that most future additions to
GDP will be generated there. Hence the growing
number of households who can afford cars, now and
in the future, will mainly reside in large cities, but the
congestion resulting from the increasing size of highdensity cities will preclude much growth in vehicular
traffic.
Vol 9 No 2 June 2000 Road & Transport Research
Urban congestion is not the only threat to rising car
use. Probably by the second decade of the new
century, rising oil prices and the need for cuts in
greenhouse gas emissions will further check traffic
growth. Given its low reserves of oil, including nonconventional sources, Asia is not well-placed to rely
on an oil-based transport system. Further, Asia’s
rising greenhouse gas emissions, including those
from transport, will soon be too large to ignore. Early
in the new century, industrialising Asia will probably
be required to curb them.
Continuation of existing car-oriented transport
policies will serve Asia poorly in the new century.
Rising travel demands in the largest, most congested
Asian cities will usually be best met by electric
heavy-rail systems, which are both far more landuse and energy efficient than car-based transport,
and may even be faster in very congested areas. In
less congested cites, both large and small, busway
systems can make efficient use of scarce road space
at modest cost. Road user charging in congested
cities can not only raise revenue, but also reduce air
pollution and fuel consumption. Such policies need
to be complemented by more stress on non-motorised
modes. To ensure the safety of non-motorised travel,
constraints on vehicular traffic will probably be
needed, possibly including peak speed reductions.
REFERENCES
ABARE (1999). Australian Commodities, 6 (3), p. 478.
ALLPORT, R. (1996). Transport management: private
demands and public needs. In: Stubbs, J. and Clarke, G.
(eds), Megacity Management in the Asian and Pacific Region,
Proceedings of a Regional Seminar, 24–30 October 1995,
Manila, Asian Development. Bank, Manila.
APELBAUM CONSULTING GROUP (1997). The Australian
Transport Task, Energy Consumed and Greenhouse Gas
Emissions, Volume B: Report, Commonwealth of Australia,
Canberra.
ATTANASI, E. and ROOT, D. (1995). Petroleum reserves
(oil and gas reserves). In: Bisio, A., Boots, S. (eds),
Encyclopedia of Energy Technology and the Environment, 2264,
John Wiley and Sons, New York.
AUSTRALIAN BUREAU OF STATISTICS (ABS) (1997).
CData 96, CD ROM, Commonwealth of Australia, Canberra,
(Also results for earlier censuses.)
BALLEW, P. and SCHNORBUS, R. (1993). Assessing
global auto trends, March/April, Federal Reserve Bank of
Chicago, p. 15.
Car travel: Asia cannot follow Australia's path. Part 2
39
BIRK, M. and REILLY-ROE, P. (1991). The effects of
transportation sector growth on energy use, the
environment and traffic congestion in four Asian countries.
In: Greene, D., Santini, D. (eds), Transportation and Global
Climatic Change, p. 91, American Council for an Energyefficient Economy, Washington DC.
BLACK, A. (1995). Urban Mass Transportation Planning,
McGraw-Hill, New York.
BOSE, R. (1996). Energy demands and environmental
implications in urban transport — case of Delhi, Atmospheric
Environment, 30 (3), p. 403.
CALDER, K. (1996). Asia’s empty tank, Foreign Affairs,
75 (2), p. 55.
CAMPBELL, C. and LAHERRERE, J. (1998). The end of
cheap oil, Scientific American, March, p. 60.
DARGAY, J. and GATELY, D. (1997). Vehicle ownership to
2015: implications for energy use and emissions, Energy
Policy, 25 (14–15), p. 1121.
NAVIN, F. et al. (1994). Road safety in China, Transportation
Research Record, 1441, p. 3.
NEWMAN, P. and KENWORTHY, J. (1989). Cities and
Automobile Dependence: An International Sourcebook, Gower,
Aldershot, UK.
NEWMAN, P. and KENWORTHY, J. (1999). Sustainability
and Cities: Overcoming Automobile Dependence, Island Press,
Washington DC.
ORGANISATION FOR ECONOMIC COOPERATION
AND DEVELOPMENT (OECD) (1999). Economic Outlook
66, OECD, Paris.
REPLOGLE, M. (1992). Bicycles and cycle-rickshaws in
Asian cities: issues and strategies, Transportation Research
Record, 1372, p. 76.
SMIL, V. (1997). China’s environment and natural resources.
In: Hudson, C. (ed.), The China Handbook, p. 188, Fitzroy
Dearborn Publishers, Chicago.
DRENNEN, T. AND ERICKSON, J. (1998). Who will fuel
China? Science, 279, p. 1483.
STATE STATISTICAL BUREAU (1998). China Statistical
Yearbook 1998, No. 17, China Statistical Publishing House,
Beijing.
EUROMONITOR (1998). International Marketing Data and
Statistics 1998, 22nd Edition, Euromonitor, London.
TAYLOR, A. (1997). Danger: rough road ahead, Fortune,
March 17, p. 37.
FAR EASTERN ECONOMIC REVIEW (1997). Asia 1998
Yearbook: a review of events in 1997, Hong Kong.
THOMAS, C., FERGUSON, E., FENG, D. and DEPRIEST,
J. (1992). Policy implications of increasing motorization for
nonmotorized transportation in developing countries:
Guangzhou, Peoples Republic of China, Transportation
Research Record, 1372, p. 18.
GARDNER, G. (1992). A study of high capacity busways in
developing cities, Proceedings of the Institution of Civil
Engineers Transport, 95, August, p. 185.
GARDNER, G. (1997). Preserving global cropland. In:
Brown, L. et al., State of the World 1997, p. 42, Earthscan
Publications, London.
GOODLAND, R. (1994). Urgent need for environmental
sustainability in land transport in developing countries: an
informal view, Transportation Research Record, 1441, p. 44.
INTERNATIONAL ENERGY AGENCY (IEA) (1997).
Indicators of Energy Use and Efficiency, OECD/IEA, Paris.
UNITED NATIONS (1997). Statistical Yearbook, 1997, 42nd
edn, UN, New York. (Also earlier editions.)
UNITED NATIONS (1999). Economic and Social Survey of
Asia and the Pacific 1999, UN, New York. (Also earlier
editions.)
UNITED STATES DEPARTMENT OF ENERGY (1998).
Annual Energy Review 1998, US Department of Engergy,
Washington DC.
–– (1998). World Energy Prospects to 2020 , OECD/IEA, Paris.
WHITE, P. (1995). Public Transport: Its Planning, Management
and Operation, 3rd edn, UCL Press, London.
JAPAN STATISTICAL ASSOCIATION (1998). Japan
Statistical Yearbook 1998, Statistics Bureau, Tokyo. (Also see
earlier editions.)
WORLD BANK (1997). China 2020: Development Challenges
in the New Century, World Bank, Washington DC.
KUTOBA, H. (1996). Traffic congestion: a tale of three
cities, The Wheel Extended: Toyota Quarterly Review, 96.
WORLD BANK (1998). World Development Indicators 1998,
Oxford University Press, New York. (Also earlier editions.)
LEWIS, N. (1994). Road Pricing: Theory and Practice, 2nd
edn, Thomas Telford, London.
WORLD BANK (1999). World Development Report 1999/
2000, Oxford University Press, New York. (Also earlier
editions.)
MORIARTY, P. and HONNERY, D. (1999). Slower, smaller
and lighter urban cars, Proceedings of the Institution of
Mechanical Engineers, 213, Part D, p. 19.
WORLD RESOURCES INSTITUTE (1996). World Resources
1996–7, Oxford University Press, New York.
NATIONAL STATISTICAL OFFICE (1998). Statistical
Yearbook Thailand, 1997, No. 17, Bangkok, Thailand.
NAVIN, F., BERGAN, A. and JINSONG, Q. (1994).
Fundamental relationship for roadway safety: model
for global comparisons, Transportation Research Record,
1441, p. 53.
WRIGHT, P. (1996). Highway Engineering, 6th edn, John
Wiley and Sons, New York.
XIN C.J. (1996). Bicycle transportation in Shanghai: status
and prospects, Transportation Research Record, 1563, p. 8.
Vol 9 No 2 June 2000 Road & Transport Research
Car travel: Asia cannot follow Australia's path. Part 2
40
Dr Patrick Moriarty
is a Research Associate in the Mechanical Engineering Department, Monash
University, Caulfield Campus. A civil engineer by training, his research interests
include energy, transport and land use policy. He recently edited a special issue on
Alternative Fuels and Power Systems for the International Journal of Vehicle Design.
Contact
Dr Patrick Moriarty
Department of Mechanical Engineering
Monash University
900 Dandenong Road
Caulfield East VIC 3145
Australia
Tel: +61 3 9903 2584
Fax: +61 3 9903 2766
Email: patrick.moriarty@eng.monash.edu.au
Vol 9 No 2 June 2000 Road & Transport Research
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