
2 REVIEW OF KEY 
PERFORMANCE INDICATORS 
IN THE TRANSPORTATION 
SECTOR 
Due to the constant increase in EC by the transport 
sector, countries had been implementing measures to 
reduce its consumption. The measures can be 
categorized in technological  or  cleaner vehicles 
strategies and Optimization or mobility management 
strategies. The first one tries to promote new 
technologies that use less energy/more efficient, 
which includes establishment of limits over transport 
companies. Equally important, the Optimization  or 
mobility management strategies optimize the way of 
energy use. This means that they change the 
mobility patterns by promoting public transport, 
connectivity between modes, a higher vehicle’s 
occupancy and the use of alternative modes. A 
research conducted by Victoria transport Policy 
Institute from Canada found that mobility 
management strategies generally achieve more 
planning objectives than cleaner vehicle strategies, 
particularly if cleaner vehicle strategies have 
rebound effects (Bosseboeuf and Richard, 1997; 
Litman, 2013; Litman, 2007; Usón et al., 2011).  
Rebound effects, also called take back effects, refer 
to the increase in car use that result from increased 
fuel efficiency, cheaper fuels or roadway expansion 
that increases traffic speeds. 
Although there is not a standard for measuring 
EE, several studies agreed that the main inefficiency 
comes from irrational use of private vehicles inside 
and outside the cities and the lack of alternative 
sources of energy (biofuels, electricity, etc.). In 
contrast, an study performed by Usón et al., 2011 
found, that bus, regional train and on foot transport 
modes are more EE and considers several indicators, 
such as fuel consumption, infrastructure, time 
travelled and environmental cost (defined in term of 
cost for nature replacement).  
Under those circumstances, the use of private 
vehicles should be tracked (measure) and one of the 
ways to do it is by looking the availability of them. 
Indicators such as the number of vehicles per 1000 
inhabitants, reflect not only the availability but also 
the potential to implement politics to reduce the use 
of cars. Eurostat, the statistical office of the 
European Union, calculates that if users of vehicles, 
which have not being manufactured could cover 
their needs by using PT, the efficiency would 
improve by 80%, because the number of vehicles per 
1000 inhabitants will drastically decrease from 411 
to 250 vehicles (Usón et al., 2011; International 
Energy Agency, 2014).  
Indirect measurements such as the average 
income can reflect the number of vehicles per 1000 
inhabitants. Statistics from ADEME (2012) show 
that countries with low average income, such as  
Romania and countries mostly from Central and 
Easter Europe, own less than 500 cars per 1000 
inhabitants, with use below 5000 km/year. In 
contrast, countries like Finland, Slovenia, France, 
UK, Sweden, Germany and Norway, consider as 
higher income countries, have a higher average or 
equal to 700 cars per 1000 inhabitants with a use 
between 12000 and 16000 km/year (Lipscy and 
Schipper, 2013). 
Furthermore, it is required to know the 
composition of the vehicles fleet, such as the age 
distribution, type of engines, average travelled 
distance, etc., to calculate their contribution to the 
final EC. As an illustration, Sweden has the higher 
consumption per vehicle compare with Italy, which 
is caused by powerful cars and lower share of diesel 
engines. On the contrary, Italy has least powerful 
cars with a high percentage of diesel engines.  
Consequently, the average car size, horsepower and 
the percentage share of diesel are important factors 
on the EE calculation (International Energy Agency, 
2014; Kaparias and Bell, 2011). 
Energy Consumption (EC) not only happens 
during the travelled time, in fact, there is an energy 
cost on manufacture, maintenance, recycling and the 
city infrastructure (roads and parking places etc.) 
(Usón et al., 2011; Ministry of ecology and 
sustainable Development and energy, 2014). Thus, 
the EC/carbon footprint (CFP) of vehicles should be 
calculated having into account its life cycle as well 
as its performance on the road.  
As it was mentioned before, energy saving can 
be achieved by increasing the efficiency on the 
technical performance of the vehicle (technological 
or cleaner vehicles strategies). Similarly, decreasing 
the car size and/or horsepower, increasing the 
average vehicle occupancy, or transforming driving 
behaviour can also lead to savings in different 
proportions. However, vehicles that are more 
efficient, are connected with regressions in driving 
behaviour, by a growth in the number of vehicles 
and the travelled kilometres; therefore, overall 
consumption tends to rise (Bosseboeuf and Richard, 
1997). To demonstrate this issue, Japan has one of 
the most efficient transport systems, besides, it has a 
high amount of mini-cars with average occupancy of 
one, and the average fuel use per passenger-km is 
similar to US, Japanese cars uses about 15% less 
DefinitionofKeyPerformanceIndicatorsforEnergyEfficientAssessmentintheTransportSector
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