On a per passenger
per kilometer basis, how do forms of transit stack up against each other. Put differently, in trying to minimize a
personal fuel footprint, what chooses should we make when given options? Which
is safer? More comfortable? More fun?
Perhaps not
the easiest questions to find an answers for but given that such questions may
well influence people in the choice of transit that they prefer it is worth the
exploration. Piecing out the impact of
personal transport from freight transportation is not easy. Total fuel use also supports recreational,
industrial, agricultural and other activities which are often included in
attributions of fuel consumption for greenhouse gas emissions. Having flagged
the caution, fasten your seatbelts for a bumpy but interesting ride.
Canadian
transportation sector information can be accessed at Natural resources Canada in a distinctly unfriendly user
format. Buried in the data are estimates
of energy consumption per passenger kilometer (expressed as Megajoules per
passenger kilometer.
efficiency MJ/PKm
|
Efficiency compared
to passenger vehicle (higher is better)
|
Proportion of total
energy consumption
|
|
Cars
|
1.88
|
1.0
|
45%
|
Buses
|
School - 0.43
Urban – 1.67
Intercity – 0.77
|
4.4
1.1
2.4
|
1%
2.4%
0.3%
|
Motorcycles
|
1.76
|
1.1
|
0.4%
|
Light trucks
|
2.36
|
0.80
|
34%
|
Rail
|
1.97
|
0.96
|
0.2%
|
Air
|
1.45
|
1.3
|
16%
|
Wikipedia
in quoting a US Energy Data Book would put intercity rail as the most
efficient, at about 40% better than cars, with other forms of rail transit
where stopping and starting are involved, slightly less efficient. Air transit comes in 25% more efficient. Urban buses at 18% less efficient
(presumably due to lower ridership than full capacity). Wikipedia energy efficiency.
The full energy data book can be found at US Energy Data Book 2011
Table 2.12 provides 2011 estimates with a well stated cautionary note on
trying to develop comparisons.
Notable in the
US figures is that energy efficiency for most forms of transport has improved
considerably over the past few decades, averaging about 1% per year per
passenger-km for cars, 1.3% for rail, and a whopping 3% per year for air
transit. The efficiency of transit
buses is reported as having remained constant on a vehicle-km basis, but
declined due to reduced ridership. Canadian
efficiency figures are harder to interpret but rightly appear to parallel US
efficiency measures.
The
distinctly different pattern of efficiency combined with utilization between
the countries is provided as a caution in making generalizable international
comparisons. Having said that, globally
total greenhouse gas emissions are attributed as 74% on road, 12% in air, 10%
marine, and 4% by rail. These numbers
are inclusive of freight and passenger transport.
An older
Australian report with dated material from 80s and 90s attempted to compare safety of
various
modalities, placing air, bus and rail at a fraction of the risk from
travel in a car (respectively at about 1%, 15% and 20%). Comparatively motorcycle travel was about 20
times more risky, bicycling at 8 times, and walking about 15 times. Recent comparative information would be
welcomed if someone is aware of a source
(contact drphealth@gmail.com ) .
The comparative risks would appear to carry some face value and better domestic
data would be useful.
May 15: A follower directed DrPHealth to a CJPH article from November 2012 that attempted to compare Canadian rates and these provide some relative comparisons that confirm the relative safety of driving, cycling and walking.
|
Fatalities per 100,000 population
|
Fatalities per 100 Million person-trips
|
Fatalities per 100 Million km
|
Injuries per 100 M person-trips
|
Injuries per 100 M km
|
Driver and Passengers
|
7.3
|
9.6
|
0.97
|
713
|
72
|
Pedestrians
|
1.7
|
14.7
|
7.4
|
392
|
196
|
Bicyclists
|
0.2
|
13.8
|
2.6
|
1398
|
264
|
Motorcyclists
|
1.1
|
|
|
|
|
Nothing was
located about the relative social value of various forms of mass passenger transport. Comparisons of noise exposure for users are
also lacking. Likewise are impacts on non-commuters in proximity to
transportation channels. (there are studies of noise exposure near airports,
sleep disruption near railways, air pollution exposure near roadways that
collectively may inform the discussion on total impacts for non-commuters as a
separate issue)
While
inherently mass transit is passive to the user, as noted in the posting on
public transit, there appears to be an inherent value in the exertion required
to move to and from access to the transportation unit, and for those
frequenting airports some would say a rigorous exertion, others might note that
most car transport is associated with minimal out of vehicle exertion. However in presenting a comparative analysis,
the lack of comparability on issues that contribute to health and wellbeing is
notable. Lacking also is good
information on the decision processes that normalize daily routines around
specific forms of transit, or those factors that contribute to longer distance
transit choices.
For some
the choice in which form of transportation to use may be limited. For many the decision is based on existing
routines. Hence research on factors
affecting decisions, comfort, ways to improve socialization and ways to
increase activity while in transit can and should supplement work on energy
efficiency and safety. One of the best examples is the Stockholm subway effort
to increase users selecting the stairs over escalators. Enjoy viewing at Piano stairs.
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