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City Energy Efficiency Report: Transport Sector Wuhan August 2015 Wuhan Integrated Transport Development Project Team

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City Energy Efficiency Report: Transport Sector

WuhanAugust 2015

Wuhan Integrated Transport Development Project Team

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Table of Contents

Glossary 4

Preface 5

Executive Summary 6

1. Introduction 10

2. Background 12

3. Transport Sector Energy Efficiency Evaluation 18

4. Potential Energy Cost Savings 24

5. Energy Efficiency Recommendations 25

Annex 1: Detailed Recommendations from TRACE 28

Annex 2: List of City Abbreviations for Cities in the TRACE Database 81

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Glossary

BRT Bus Rapid TransitCNG Compressed Natural GasESMAP Energy Sector Management Assistance ProgramETC Electronic Toll CollectionGBP British PoundGHG Greenhouse gasesGJ GigajouleGWh Gigawatt hourHDI Human Development IndexICT Information and Communication TechnologyITS Intelligent Transport SystemsKPI Key Performance IndicatorkWh Kilowatt hourLEZ Low-Emission Zone MJ Mega jouleNMT Non-Motorized Transport (Cycling and Walking)NMV Non-Motorized Vehicle RMB Renminbi (Chinese Currency)SCE Standard Coal EquivalentSD Singapore DollarTRACE Tool for Rapid Assessment of City EnergyUSD US Dollar

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Preface

The Tool for Rapid Assessment of City Energy (TRACE) is a decision-support tool designed to help cities quickly identify underperforming sectors, evaluate improvement and cost-saving potential, and prioritize sectors and actions for energy efficiency intervention. TRACE1, developed by the Energy Sector Management Assistance Program (ESMAP), offers a range of potential solutions, along with implementation guidance and case studies. This report specifically focuses on citywide energy performance and diagnoses of potential energy savings in the transport sector in Wuhan, China.This report was prepared the Wuhan Integrated Transport Development Project team of The World Bank’s Transport and Information and Communication Technology (ICT) East Asia and Pacific Unit. The team, led by Arturo Ardila-Gomez (Lead Transport Economist), included Li Qu (Young Professional), Gladys Frame (Consultant), and Yang Chen (Urban Transport Specialist). The financial and technical support by ESMAP is gratefully acknowledged. ESMAP—a global knowledge and technical assistance program administered by the World Bank—assists low- and middle-income countries to increase their know-how and institutional capacity to achieve environmentally sustainable energy solutions for poverty reduction and economic growth. ESMAP is funded by Australia, Austria, Denmark, Finland, France, Germany, Iceland, Japan, Lithuania, the Netherlands, Norway, Sweden, Switzerland, the United Kingdom, and the World Bank Group.

1 More information on TRACE can be found at http://www.climateplanning.org/tools/tool-rapid-assessment-city-energy-trace

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Executive Summary

As a result of rapid development, cities in China are experiencing ever-increasing levels of energy consumption that is forcing them to consider and plan their development in a sustainable manner. Transport, one of the most energy dependent sectors, accounted for 37 percent of petroleum consumption in China in 2013. This number has increased significantly over the past few years. Energy savings in the transport sector play an important role in sustainable city development in terms of relieving congestion and reducing greenhouse gases (GHG).

Wuhan is a rapidly growing metropolitan area. In 2013, with a population of 10.22 million, it ranked as the sixth-most populous city in China. Amid extensive construction of infrastructure and ongoing development, the city is seeking strategies to achieve optimal energy efficiency. The World Bank team analyzed energy efficiency across the city, including in the transport sector. Key findings include:

• Relatively high citywide primary electricity consumption per capita;• Relatively high citywide energy consumption per capita;• The average length of high capacity transit routes per 1,000 people is low; • High private transport energy consumption; and• Total transport energy use per capita, public transport energy consumption, and public transport mode split ranks in the middle when compared with peer cities.

According to the diagnostic results, it is estimated that potentially 31 percent can be saved in public transport energy costs and 20.2 percent in private vehicles’ energy costs.

SectorEstimated Percentage

of Energy Consumption

Reduction

Energy Cost(USD)

Potential Energy Cost Savings

(USD)

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Public Transportation 31.0% 253,006,268 78,437,455

Private Vehicles 20.2% 989,163,063 169,925,734

Based on Wuhan’s specific situation, the TRACE tool provided the following recommendations for energy savings in the transport sector:

• Enforcement of vehicle emissions standardsEnforcement of vehicle emissions standards not only improves local air quality, it also leads to lower fuel consumption. Vehicle emissions standards may be implemented through mandatory regular emissions checks. The higher the vehicle emissions standard, the less fuel the vehicle is likely to consume and the higher the reductions in the emission of fine particles, nitrogen dioxide, ozone, CO2 and other pollutants. Lower emissions result in better air quality and a lower risk of respiratory diseases associated with air pollution.

• Traffic flow optimizationTraffic can be positively managed to ensure the most efficient operation of the transport system. Management techniques and Intelligent Transport Systems (ITS) will seek to minimize distance travelled between origin and destination, minimize the number of vehicle stops, ensure the efficient flow of traffic, and encourage multiple occupancy vehicle travel. The strategy will encourage efficient use of vehicles and minimize journey lengths and vehicle stops thereby reducing fuel use.

• Public transport developmentDevelop or improve the public transport system and take steps to increase its accessibility and use. Public transport achieves lower emissions per capita than private cars and has the potential to provide an equitable transport network. A reduction in the number of private vehicles in circulation can lower emissions and improve air quality.

• Non-motorized transport modesNon-motorized transport modes have zero operational fuel consumption and require low capital costs for implementation. In

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addition to improving the health of users, their use reduces noise pollution and improves air quality. The benefits include improved air quality, lower operating costs for users and providers, and lower infrastructure requirements. However, it should be noted that in Chinese cities, the term “Non-Motorized Vehicle (NMV)” covers electric bicycles (E-bikes) and their numbers have risen substantially since motorcycles were banned in many urban areas. Vehicle registration data for Wuhan in 2012 shows E-bikes at 0.7million and bicycles at 1.17million. In Wuhan in 2008, E-bikes comprised 13% of the trip modal split with bicycles comprising 7%2.

• Parking restraint measuresRestricting parking can discourage car use and provide an incentive to use more sustainable modes of transport, including public transport. Removing vehicles from circulation reduces fuel use and the effects of congestion.

• Traffic restraint measuresDiscouraging potential drivers from using their cars can lead to fewer cars in circulation. This can encourage people to use alternative modes, which in turn will increase their viability (increased public transport patronage, for example). Removing vehicles from circulation reduces fuel use and the need for road space.

• Congestion chargingCongestion charging restrains access by selected vehicle types, usually private cars, into large urban areas during congested times of the day. The aim is usually to discourage work-based commuting trips into a defined urban area. Measures range from complete restriction to discouragement through charging to incentive pricing for low-emission vehicles in low-emission zones. It is a market-based mechanism for influencing driver behavior that looks to capture the “external cost' of vehicle travel during congested periods of the day.

• Travel planningInforming drivers about alternative modes of transport and sharing resources with other drivers leads to fewer cars being used and 2 Wuhan Municipal Engineering Design and Research Institute (WMEDRI), 2009.

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more trips on public transport. Removing vehicles from circulation reduces fuel consumption and increases the viability and efficiency of public transport.

• Awareness-raising campaigns Public education and training campaigns can increase the public's awareness and understanding of the benefits of energy efficiency and help change attitudes. Providing information on easy ways to be more energy efficient can help modify citizen behavior and contribute to overall energy savings. The key benefits are more energy efficient behavior by residents leading to reduced energy consumption within the city. For example, encouraging people to leave their car at home and take transit instead, or promoting walking for short trips. Indirect benefits include reduced pressure on energy infrastructure, reduced carbon emissions, and better air quality.

The above recommendations can build upon the ongoing programs carried out by the city, and some of them can also be combined with the linked Wuhan Integrated Transport Development Project that is financed by World Bank.

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1. Introduction

Methodology

The team utilized the TRACE tool to evaluate potential energy savings and provide energy efficiency recommendations to the urban transport sector in Wuhan. The TRACE tool was designed to help prioritize energy savings across six sectors—transport, municipal buildings, water and wastewater, street lighting, solid waste, and power and heat. It consists of three principal modules:

1) Energy benchmarking: Compares Key Performance Indicators (KPIs) across peer cities such as percentage modal split for Non-Motorized Transport (NMT) which covers cycling and walking; 2) Sector prioritization: Identifies sectors that offer greatest energy cost savings potential; and3) Intervention selection: Provides “tried and tested” energy efficiency solutions.

For this study, only the transport sector was investigated using the TRACE tool to facilitate the linked World Bank loan project to identify energy efficiency in Wuhan. During the course of the preparation of the Wuhan Integrated Transport Development Project, the project team visited Wuhan and conducted interviews with officials from a broad range of city agencies to collect energy use information for the city as well as for the transport sector.3 The data was then fed into the TRACE tool to conduct the current energy use benchmarking with other cities in the TRACE database. The initial energy saving potential was then estimated according to the benchmark results as well as the level of the city’s control over transport sector authorities. Finally, recommendations were provided based on the energy saving evaluation and the city database. The initial energy saving potential, and assets and infrastructure, with detailed information on each of the strategies.

3 Interviewed officials in agencies, including Wuhan Transport Bureau, Wuhan Transport Strategy Planning Institute, Wuhan Traffic Management Bureau, bus company, and taxi company.

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The TRACE tool has been deployed in twenty-seven cities in Africa, Asia, Europe, and Latin America.4 It helped the cities prepare local energy efficiency measures in a low-cost and fast manner. Specifically, the measures have been implemented in Eastern Europe to reduce GHG emissions and energy related costs as part of the Europe 2020 strategy—the European Union’s jobs and growth strategy, the objective of which is to reduce GHG emissions by 20 percent by 2020.

Limitations of the TRACE tool

While TRACE is a simple and easy tool to evaluate a city’s energy efficiency, there are limitations with respect to the depth of its analysis. It estimates potential energy savings based on benchmarking against other cities in the TRACE database, but the evaluation of city specific energy savings would require more detailed data, which are difficult to obtain, especially in the transport sector. However, TRACE provides the best practices for energy saving recommendations based on the city ’s evaluation with cost and implementation requirement information, but it does not provide city specific details on the costs required to undertake the recommended strategies.

2. The Wuhan Case Study

Wuhan, located in central China, is home to 10.22 million residents, covers 8494.41 square kilometers, and had an annual Gross Domestic Product of RMB905.13 billion (USD145.99 billion) in 2013.5 Although Wuhan is one of China’s fastest-growing cities, it lags behind the coastal cities. The disposable income per capita in Wuhan is RMB20,681 per year6

compared to RMB32,472 in eastern coastal cities.7 Thus, the Government of China launched the “Rise of Central China” program to boost economic growth in central China. Wuhan, along with eight smaller cities within a 100 km radius (1+8 city cluster), was selected as one of the first pilot demonstrations of regional planning in China. The goal was to achieve a more balanced and sustainable development pattern in these cities.

4 View full list of the cities where TRACE has been deployed: http://www.esmap.org/node/4368.5 Wuhan Statistical Yearbook, 2014.6 Calculation based on Hubei Province Statistical Yearbook, 2013.7 China Statistical Yearbook, 2014.

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Improving transport is one of the fundamentals to the development of a central China strategy. Following China’s pattern of rapid motorization, Wuhan, too, is experiencing a rapid growth in the number of motor vehicles. With about 130 vehicles per 1,000 population,8 the city suffered the negative impact of increasing congestion despite a relatively low vehicle ownership rate compared to other cities such as London (300) and cities in the Netherlands (500)9. The quality of the environment is compromised by air pollution from the growing private vehicle fleet and old public transport vehicles

3. Background

Wuhan is one of the largest cities in China. It ranked the sixth-most populous Chinese city in 2013, according to the China Urban Development Statistical Yearbook as presented in Table 1. As with other Chinese cities, Wuhan is experiencing rapid urbanization with an urbanized population rate of 67.6 percent in 2013 that has increased by about 4 percent since 2007.

Table 1: Top Ten Populous Cities in China10

Rank City Population (million)

1 Shanghai 23.80

2 Chongqing 20.70

3 Beijing 20.69

4 Guangzhou 12.86

5 Shenzhen 10.55

6 Wuhan 9.58

7 Tianjin 8.78

8 Chengdu 6.26

9 Dongguan 6.02

8 Calculation based on Wuhan Statistical Yearbook, 2014.9 Frame, Gladys et al, The Kingdom of the Bicycle: What Wuhan can learn from Amsterdam, to be presented at the World Conference on Transport Research - WCTR 2016 Shanghai. 10-15 July 201610 China Urban Development Statistical Yearbook 2013 data is for 2012. The population is the total of urban district population and urban district temporary population.

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10 Nanjing 5.83

Figure 1: Urbanization Rate of Wuhan 2007-201311

As an inland city, Wuhan has a typical continental climate with four distinct seasons. Wuhan is famous for its hot summers. The highest temperature can reach to above 40 degrees Celsius for continuous days in July and August. Thus, it is listed as one of the four “oven” cities in China. The Yangtze and Han Rivers divide Wuhan into three major parts: Hankou, Wuhan, and Hanyang. Due to these major rivers, as well as plenty of freshwater lakes, the weather is humid throughout the year, which makes it feel even hotter in summer and colder in winter.

Rapid development and economic growth have put pressure on land, energy, and environment. Wuhan’s total energy consumption reached 487.2 million tons Standard Coal Equivalent (SCE) in 2013.12 11 Wuhan Statistical Yearbook 2014.12 Wuhan Statistical Yearbook 2014.

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Although hydroelectric is being developed in the area, the major energy source in Wuhan is still fossil energy, which generates more GHG emissions (see Figure 2.) than clean energy sources.

Figure 2: Energy consumption by source in Wuhan, 2013

In 2013, the total electricity consumption in the city amounted to 43,723 GWh, which almost doubled compared to the amount in 2006 (see Figure 3).

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Figure 3: Total electricity consumption of Wuhan 2006-201313

The largest share of electricity consumption goes to secondary industry (57 percent), followed by tertiary industry (23 percent), residential (19 percent), and primary industry (1 percent).14 Among the total industry electricity consumption, three percent—1,162 GWh—is shared by transportation, storage, postal and telecommunication services.

13 Wuhan Statistical Yearbook, 2014.14 Defined by “China National Industries Classification”. Primary industry includes: i) farming, ii) forestry, iii) animal husbandry, iv) fishery, and v) water conservancy; secondary industry includes: i) mining and quarrying, ii) manufacturing, iii) electricity, gas, and tap water production and supply, and iv) construction; tertiary industry includes: i) transportation, storage, postal and telecommunication services, ii) information transfer, computer, and software services, iii) commerce, hotel, and catering services, iv) banking, real estate, commerce and business services, and v) public enterprise and management organization.

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Figure 4: Electricity consumption by sector in Wuhan, 2013

Citywide energy consumption benchmarking

With primary electricity consumption at 5,318 kWh per capita,15 Wuhan ranks 3rd among the cities in the TRACE database with a similar continental climate, following Toronto and Beijing, as shown in Figure 5.16 When it comes to primary energy consumption, Wuhan also ranks 3rd

among the cities with similar climate with the value of 108 Gigajoules per capita, following Toronto and Belgrade, as presented in Figure 6. Due to the specific weather features and its inland location, Wuhan requires more electricity and energy during the hot season between June and August, as well as the cold season between December and February. Thus, the city’s electricity and energy consumption ranks relatively high compare to other cities in the TRACE database.

15 Calculation based on Wuhan Statistical Yearbook, 2014.16 Refer to Annex 2 for “List of City Abbreviations for Cities in the TRACE Database.”

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Figure 5: Primary electricity consumption per capita (continental climate)

Figure 6: Primary energy consumption per capita (continental climate)

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4. Transport Sector Energy Efficiency Evaluation

In Wuhan, the total number of motor vehicles has increased rapidly over the past few years. By end of 2013, this total amounted to 1.53 million. The share of private vehicles reached 1.21 million, which accounted for 79 percent of the total.

In 2012, total petroleum consumption in China reached 4.67 million tons. The transport sector accounted for 37 percent of this consumption.17 The share of petroleum consumption by the transport sector has been increasing over the past two decades, from 15 percent in 1990 to 37 percent in 2012, as presented in Figure 7, due to rapid motorization nationwide.

Figure 7: Petroleum consumption in total and by transport sector in China

17 China Statistical Yearbook, 2014.

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Urban passenger transport in Wuhan is mainly composed of road transport, supported by water transport on the rivers. Public transport modes include bus, metro, taxi, and ferry.

Figure 8: Total number of vehicles and number of private vehicles18

18 Number of private vehicles in 2010 is missing due to lack of statistical data by vehicle type. Data source: Wuhan Transport Annual Report, 2014, by Wuhan Transport Development Strategy Research Institute.

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The Wuhan Public Transport Company operates a fleet of approximately 7,000 buses on 342 routes with a total route length of 6,314 km. Of these 7,000 buses, 4,500 are powered by diesel, 2,250 are powered by Compressed Natural Gas (CNG), and the other 250 are powered by electricity and new clean energy. All the buses are scrapped after eight years of use to keep the fleet relatively new. In 2013, there are three metro lines operating in the city with a total length of 96.7 km. In 2013, the total number of passengers who travelled by public transit per day was 5.92 million, of which 5.1 million (86 percent) travelled by buses and 0.8 million (14 percent) by metro.19,20

As one of the pilot cities in the National Transit Metropolis Initiative, Wuhan’s transit system is currently undergoing an unprecedented pace of development. It is expected that six additional metro lines and eight Bus Rapid Transit (BRT) lines will open by year 2020.

19 Wuhan Transport Annual Report, 2014, by Wuhan Transport Development Strategy Research Institute.20 By end of 2013, only two metro lines were opened in Wuhan with a total length of 62.6 km.

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There are 15,637 taxis in Wuhan that carried 420 million passengers in 2013. The major power sources for transport are gasoline, diesel, and compressed natural gas (CNG). By the end of 2014, 98 percent of the taxis in Wuhan were CNG vehicles.

According to the resident travel survey in 2013, 23 percent of the trips were taken by buses; 7 percent by metro; 6.5 percent by taxi; 20 percent by private cars; 18.5 percent by bicycle, including E-bikes; and 25 percent by walking,21 as shown in Figure 9.

Figure 9: Trip mode split in Wuhan

Transportation Sector Benchmarking

According to the analysis by the TRACE tool, 5,304.63 Mega joules/capita transportation energy use places Wuhan in the lower middle of the TRACE database with comparable cities with similar Human Development Indicator (HDI) as shown in Figure 10. This calculation is based on total vehicle ownership, total population in Wuhan Statistical Yearbook 2014,

21 Project Appraisal Document of Wuhan Integrated Transport Development Project.

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average travel distance, average fuel consumption per 100 km, and rate of vehicles on road provided by local agencies.

Figure 10: Total transportation energy use per capita

Although Wuhan opened its first metro line in 2004, metro system development has only been boosted in the past few years. Currently, with three metro lines of a total length of 96.7 km at the end of 2014, there are 11.7 meters of high-capacity transit per 1,000 people. This ranks Wuhan in the lower end among the cities in the TRACE database with similar HDI, a bit lower than Gaziantep and Mexico City, but higher than Yerevan, Jakarta, Quezon City, Tehran, and Bogota. According to the current metro system plan, nine metro lines will be opened by end of 2020 and the total length will reach to about 400 km.

Figure 11: Meters of high-capacity transit per 1,000 people

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With a 30 percent public transport mode split, Wuhan ranks in the lower middle among the cities in the TRACE database. This ranking is expected to improve over the next few years as more metro lines and BRT are built. According to the target value proposed by the National Transit Metropolis Initiative, the public transport mode split in the pilot cities (Wuhan is in the first batch of the pilot cities) should reach at least 50 percent in five years, by 2020.

Figure 12: Public transportation mode split

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It is estimated that among the total transport energy consumption in Wuhan, 16.6 percent was by public transport and 64.9 percent by private cars.22 The public transport energy consumption in Wuhan is about 0.51 MJ/passenger km, ranking at the lower middle among comparable cities, a little higher than Rio de Janeiro and lower than Guangzhou.

Figure 13: Public transport energy consumption

Private transport energy consumption in Wuhan, however, placed the city at the higher middle among cities in the TRACE database with the value of 2.14 MJ/passenger km, the same level as Johannesburg and Bogota. Compared to 0.51 MJ/passenger km energy consumption by public transport, private transport consumes about four times more energy than public transport. Thus public transport promotion should be one of the key strategies to achieve energy savings.

Figure 14: Private transport energy consumption22 Calculated based on total number of vehicles, total energy consumption by transport sector in Wuhan Statistical Yearbook, 2014, average travel distance, passenger km provided by local agencies.

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5. Potential Energy Cost Savings

Based on the initial results provided by the TRACE energy-benchmarking module, the potential energy reduction value is calculated as the mean of the values of all chosen peer cities with better energy performance. Thus, for Wuhan, potentially 31 percent energy use can be saved for the public transport sector, and 20.2 percent energy use can be saved for the private transport sector. The energy expenditure for public transport and private vehicles is estimated based on the total amount of fuel consumption and the average cost of the fuel.

As public transportation in Wuhan is operated by the public sector, the city authority has total control over the public transport sector to implement proposed energy saving strategies. Private vehicles are strongly regulated and managed by city authorities. The city also creates and enforces regulations. Thus the city authority control index over private vehicles is set as 85 percent as recommended by TRACE.

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Potential energy cost savings are calculated based on the above assumptions. The results are presented in Table 2. It shows that about USD78 million can be saved by public transportation and USD170 million can be saved by private vehicles in terms of energy cost. As an initial estimation of energy cost savings based on energy performance benchmarking these savings could be potentially achieved by implementing appropriate energy saving strategies as stated in the next section.

Table 2: Estimated energy cost savings for public transport and private vehicles in Wuhan

Sector

Estimated Percentage of Energy

Consumption Reduction

Energy Cost(USD)

City Authority Control

Potential Energy Cost

Savings(USD)

Public Transportation 31.0% 253,006,268 1.00 78,437,455

Private Vehicles 20.2% 989,163,063 0.85 169,925,734

6. Energy Efficiency Recommendations

Based on the initial energy saving evaluation, TRACE contains a playbook of energy efficiency recommendations applicable for each of the sectors. According to the specific situation in Wuhan, viable recommendations towards energy savings in the transport sector are selected as below in Table 3.

Table 4 presents the first cost and potential energy savings for each of the recommendations. The detailed recommendation description, implementation, monitoring, case studies, and guidance references are provided in Annex 1.

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Table 3: TRACE list of recommendations and implementation speed

Recommendation Implementation Speed

Enforcement of Vehicle Emission Standards > 2 years

Traffic Flow Optimization > 2 years

Public Transport Development > 2 years

Non-Motorized Transport Modes > 2 years

Parking Restraint Measures > 2 years

Traffic Restraint Measures 1-2 years

Congestion Pricing > 2 years

Travel Planning 1-2 years

Awareness-raising Campaign < 1 year

The recommendations focus on transport development as well as restraint policies to enhance energy savings. Specifically, in Wuhan, public transport development is underway with extensive metro and BRT construction; non-motorized transport modes could be enhanced by the reinvigoration of bicycle networks and improved bike-sharing programs; congestion pricing and parking restraint measures can be combined with the existing Electronic Toll Collection (ETC) system, which has been deployed for nonstop toll collection on bridges and tunnels. Other recommendations can be implemented jointly with the linked Wuhan Integrated Transport Development Project through Intelligent Transport System (ITS) development and integrated transport information center activities.

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Table 4: Energy saving recommendations with first cost and energy savings potential

First Cost

> $1,000,000 $100,000-$1,000,000 < $100,000

Ener

gy S

avin

gs P

oten

tial

>200,000 kWh/annum Public Transportation DevelopmentEnforcement of Vehicle

Emissions StandardTraffic Flow Optimization

100,000 - 200,000 kWh/annum

Non-Motorized Transport ModesCongestion Pricing

Traffic Restraint MeasuresAwareness-raising Campaign

Travel Planning

Parking Restraint Measures

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Annex 1: Detailed Recommendations from TRACE

Improving Energy Efficiency in the Transport Sector in Wuhan, China

1.Enforcement of Vehicle Emissions Standards

Description

Enforcement of vehicle emissions standards not only improves local air quality, but also leads to lower fuel consumption. Vehicle emissions standards may be implemented through mandatory regular emissions checks for vehicles.

The higher the vehicle emissions standard, the less fuel it is likely to consume and the higher the reductions in the emission of fine particles, nitrogen dioxide, ozone, CO2 and other pollutants. Lower emissions result in higher air quality and lower the risk of respiratory diseases associated with air pollution.

Attributes

Energy Savings Potential

> 200,000 kWh/annum

First Cost

USD100,000-1,000,000

Speed of Implementation

> 2 years

Co-Benefits

Reduced carbon emissions

Improved air quality

Enhanced public health and safety

Increased employment opportunities

Implementation Options

Implementation Activity Methodology

Technology-based enforcement

The city authority implements vehicle

standards via mandatory vehicle

registration using number plates, which

are monitored with automatic number-

plate recognition cameras. This

approach works most effectively in

discrete areas of the city with limited

entry and exit points (to minimize capital

costs). Whilst the initial capital costs

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may be high, operational costs are

lower than manual enforcement, though

it must also be supported by

enforcement/sanction systems.

Expansion of this approach to citywide

application is capital intensive although

more effective than the manual

approach (see manual enforcement

implementation activity below). Vehicles

that have passed the test are entered

into a database linked to the automatic

number-plate recognition cameras.

Manual enforcement

The city authority requires manual

checks of vehicle emission standards,

e.g., by traffic officers or wardens who

collect non-compliance penalties, or by

cordon officers who restrict entry into an

emission standard area. This is done

either by means of a system that uses

categorized number plates, or by use of

easily recognizable windscreen stickers

displaying the permit or pass from

emissions checks. A consideration for

either approach should be whether the

entire city should be designated for

stringent emissions standards or

whether there are particular areas that

can easily be identified for the purpose.

Note that this approach is less likely to

capture all emissions test evaders, and

is at risk from unscrupulous traffic

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officers or wardens. This intervention

requires the establishment of a network

of emissions testing centers to award

compliance certificates or permits. See

Stockholm case study for further details.

Emissions centers

The city authority regulates a network of

emissions testing centers, which are

independently assessed and verified to

undertake emissions tests. Sanctions

for abuse or fraud should be severe to

deter corruption. See Mexico City case

study for further details.

Monitoring

Monitoring the progression and effectiveness of recommendations, once implemented, is fundamental to an accurate understanding of their value over the longer term. Where the city authority implements a recommendation a target (or set of targets) should be defined that indicates the level of expected progress over a given timescale. At the same time, a monitoring plan should be designed. The monitoring plan does not need to be complicated or time consuming but should, at a minimum, cover the following aspects: identification of information sources, identification of performance indicators, a means of measurement and validating measuring equipment or processes, record-keeping protocols, a schedule for measurement activity (daily, weekly, monthly etc.), assignment of responsibilities for each aspect of the process, a means of auditing and reviewing performance, and, finally, establishment of reporting and review cycles.

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Case Studies

Low-Emission Zone, London, UK

Source: Transport for London (2009). “Cleaner air for Greater London—The Low-Emission

Zone is now in operation,” available online at:

http://issuu.com/baumot/docs/lez-information-leaflet

Further information can be found at:

https://tfl.gov.uk/corporate/publications-and-reports/low-emission-zone

The aim of the program is to improve air quality in the city by deterring the most

polluting vehicles from driving in the area. The vehicles affected by the Low-Emission Zone

(LEZ) are older diesel engine lorries, buses, coaches, large vans, minibuses, and other

heavy vehicles that are derived from lorries and vans. The LEZ is enforced using fixed and

mobile cameras, which read vehicles’ registration number plates as they drive within the

zone. This is then checked against a database of registered vehicles, which meet the LEZ

emissions standards and which are exempt from a daily charge. If the vehicle does not

meet required emission standards or does not qualify for an exemption, the daily charge

has to be paid. A critical issue in the successful operation of LEZ schemes is the

implementation of an effective enforcement program. If a vehicle driving within the zone is

identified as not meeting the LEZ emission standards and no daily charge has been paid, a

Penalty Charge Notice is issued to the vehicle's registered keeper. Transport for London,

the London transport authority, works together with a European debt recovery agency and

has established links with many European vehicle-licensing agencies in order to recover

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penalties against vehicles registered outside Great Britain.

Environmental Zone, Stockholm, Sweden

Source: Transport & Travel Research (2006). “Air Quality Impacts of Low-Emission

Zones,” available online at

http://www.iaqm.co.uk/text/resources/reports/lez_aq_impacts.pdf

Environmental zones were created in central areas of Stockholm, which were

particularly sensitive to emissions and noise. Based on vehicle age, the approach is simple:

all vehicles over 3.5 tons that are older than eight years, including buses, are banned.

(Exceptions are made for vehicles between eight and 12 years old if they are retrofitted with

new engines). Enforcement is achieved through the police via spot checks as well as an

informal arrangement between carriers. Identification of potential violators happens by

means of the vehicle number plate, with older vehicles being required to carry permits to

prove they have been retrofitted with emissions-standard approved technology. The zone

has resulted in older vehicles being replaced earlier than they otherwise would have been,

yielding significant reductions in the levels of key pollutants.

Inspection Program, Mexico City, Mexico

Source: Kojima, M. and Bacon, R. (2001). “Emission Control: Public Policy for the Private

Sector.” Note No. 238, available at

https://www.wdronline.worldbank.org/handle/10986/11365

All motorists have to display a sticker showing that their vehicle has passed an

emissions test every six months or risk a fine. In its earlier stages of deployment this policy

suffered from high levels of evasion—an implementation problem common to similar

programs in developing countries. However, as a result of operating through high-volume,

test-only centers that are operated by the private sector, program performance has greatly

improved. It is estimated that the program has achieved an energy savings potential of

approximately 5 percent. Experiences recommend optimizing the number of centers

relative to the volume of traffic to be tested, thereby reducing the risk of the tests becoming

less rigorous as each center relaxes its inspection protocols in order to attract more

customers to increase market share. Each lane in the road section, which generates

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$10,000 per year, had a capital cost of approximately USD60,000.

Tools and Guidance

USAID (2004). “Vehicle Inspection and Maintenance Programs: International Experience and Best Practices.” This document consolidates the details of implementing a vehicle inspection and maintenance program, and provides an overview of lessons from a range of best practice international experiences. Available online at http://pdf.usaid.gov/pdf_docs/PNADB317.pdf .

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2.Traffic Flow Optimization

Description

Traffic can be positively managed by reducing the number of stops to ensure the most efficient operation of the transport system. Management techniques will seek to minimize distance travelled between origin and destination, ensure the efficient flow of traffic, and encourage multiple occupancy vehicle travel.

Encourage the efficient use of vehicles and minimize journey lengths, reducing fuel use.

Attributes

Energy Savings Potential

> 200,000 kWh/annum

First Cost

USD100,000-1,000,000

Speed of Implementation

> 2 years

Co-Benefits

Reduced carbon emissions

Enhanced public health and safety

Implementation Options

Implementation Activity Methodology

Flow optimization and reduction of the number of stops

The city authority changes driving

patterns either by technical optimization

of traffic signaling, or by the provision of

information. Real-time information can

be provided by means of Variable

Message Signing (VMS) or

telecommunication where drivers are

provided with route-switching options,

clear directional signing to destinations,

and directions to nearest available car

parks. This minimizes journey length

and reduces congestion. Messaging

systems have also been used to

counter crime by providing information

on, e.g., kidnappings and terrorist

attacks. See Portland and Milton

Keynes case studies for further details.

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Regulatory

The city authority establishes high-

occupancy vehicle (HOV) lanes,

producing an incentive for car sharing.

The pairing of users can be left to civic

initiatives, or driven by city authorities

either separately or in combination with

its other initiatives (in the latter case,

initiatives can be communicated to

users using the same platform).

Achieving a minimum number of users

is crucial as insufficient use results in

reduced available road space and

increased congestion. The

implementation of an effective

enforcement and penalties system is

equally important as the lane will

otherwise attract an unacceptably high

level of non-HOVs, which also reduces

effectiveness. See Madrid case study

for further details.

Monitoring

Some suggested measures that relate specifically to this recommendation are as follows:

Perform traffic surveys of number of vehicles in circulation by using traffic counters; and

Determine mode share of people travelling in the area or city.

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Case Studies

Arterial “Green Wave” Traffic Flow Optimization, Portland, USA

Source: C40 Cities (2010). “Portland, USA: Optimizing Traffic Signal Timing Significantly

Reduces the Consumption of Fuel,” available online at

http://www.c40cities.org/bestpractices/transport/portland_traffic.jsp .

The city authority optimized traffic signal timing at 135 intersections on 16 of some

of Portland's most congested thoroughfares. “Optimization” of traffic signals consists of re-

timing the signals to improve their synchronization across a road traffic network. The cost of

an intersection synchronization varied between USD1,000 and USD3,000. The resulting

reductions in the frequency with which vehicles accelerate and decelerate, as well as the

reductions in the time vehicles spend with idling engines, yielded annual fuel savings of

1,750,000 gallons of gas. This is the equivalent of removing 30,000 passenger vehicles

from the road for an entire year. The city went a step further by measuring and eliminating

CO2 through the purchase of carbon credits.

Variable Message Signs, Milton Keynes, UK

Source: Department for Transport (2010). “Case Study: Milton Keynes Integrated Traffic

Management,” available online at http://www.dft.gov.uk/itstoolkit/CaseStudies/milton-keynes-

integrated-traffic-management.htm .

In order to achieve a more efficient usage of car parks and encourage shoppers into

the central retail area of Milton Keynes, as well as reduce congestion caused by cars

looking for parking, the city administration invested in Variable Message Signs that display

the location and availability of parking spaces to road users. Installation costs were lowered

by making use of the existing ducted network in Milton Keynes used by the police for

CCTV. This created the added benefit of providing a large capacity network for future

growth in data transmissions. The reduction in congestion and delays resulting from the

system are estimated to save motorists and bus passengers in the central area more than

GBP3 million over a 10-year period.

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High-Occupancy Vehicle Lane, Madrid, Spain

Source: Monzon, A. (1999). “Managing long term congestion in HOV lanes. Effect of 2+ vs.

3+ limit on the Madrid N-VI corridor.” Paper presented at the European Transport

Conference, Cambridge, January 1, 1999, available online at

http://abstracts.aetransport.org/paper/index/id/914/confid/5

High environmental standards, low housing density, and high motorization rates influenced

the decision to implement an HOV-lane scheme on the median of the N-VI motorway into

Madrid. Finally, in 1995, median reversible HOV lanes were opened. The cutoff limit for the

lane is 2+ passengers and the facility is separated from the mix-flow lanes by a concrete

barrier along its entire length. A successful design aspect is the reversible basis on which

the system operates to match peak flows, serving the inbound trips during the morning

peak and the outbound trips during the evening peak. Rather than increase ridesharing, the

lanes have attracted a growth in public transport mode share (40 percent in the period

0700-1000 in the year following implementation), resulting in increased frequencies of

services.

Tools and Guidance

Colorado Department of Transportation (2005). “CDOT Guidelines on Variable Message

Signs (VMS).” A guidance document for the design of Variable Message Sign (VMS)

messages. Available online at http://www.cotrip.org/its/whitepapers/VMSGUIDE-rev-

2005.pdf

Alabama Department of Transportation (2007). “Traffic Signal Design Guide & Timing

Manual.” A guidance document with detailed guidelines and recommendations for the

designing and timing of traffic signals in the State of Alabama. Available online at

http://www.dot.state.al.us/maweb/frm/ALDOT%20Traffic%20signal%20Design%20&

%20Timing%20Manual.pdf

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3.Public Transport Development

Description

Develop or improve the public transport system and take measures to increase its accessibility and use. Public transport achieves lower emissions per capita than private cars, and has the potential to provide an equitable transport network. A reduction in the number of private vehicles in circulation can lower emissions and improve air quality.

Attributes

Energy Savings Potential

> 200,000 kWh/annum

First Cost

> USD1,000,000

Speed of Implementation

> 2 years

Co-Benefits

Reduced carbon emissions

Improved air quality

Enhanced public health and safety

Implementation Options

Implementation Activity Methodology

Bus priority

The city authority establishes dedicated

bus priority measures. This enables

buses to bypass traffic queues

enhancing their reliability and journey

times. There are a range of measures,

including bus lanes and priority at

junctions that could be implemented.

See the Bogota case study for further

details.

Signaling

The city authority invests in the

necessary infrastructure for bus-priority

signaling. Such systems are linked to

buses via transponders that use GIS

information, and favor the circulation of

approaching buses either by extending

green lights for buses or by shortening

the cycle for cars.

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Information

The city authority provides good quality

passenger-waiting facilities as well as

good information services. The

provision of real-time bus countdown

information allows users to understand

and manage wait times. These services

enhance the attractiveness of public

transport.

Operations

The city authority invests in the

necessary infrastructure for electronic

ticketing. This allows for use of multiple

buses within a given amount of time

with one ticket, reducing the cost of

travel, putting buses within reach of the

poorest, while attracting a wider patron

base when in combination with other

modes such as heavy rail or metro.

Planning regulations and guidelines

The city authority links development

densities to public transport availability

and funding. The city authority reviews

the city’s zoning ordinances and

considers making the following

changes: Increase the permitted floor

area ratio/plot ratio on sites located

near public transport hubs. In areas

where it is appropriate, re-zone single-

use land to allow multiple uses on the

same site. Allowing higher densities of

development along well-served public

transport corridors creates a patron

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base for public transport and can be

used in combination with other planning

measures, such as capping parking

provision to residential and office

buildings, thus discouraging car use.

Developers are required to show how a

new development links to the existing or

planned public transport network in

order to gain planning permission. See

the Curitiba case study for further

details.

Subsidies

The city authority subsidizes travel on

public transport. In certain areas, this

can provide an incentive for people to

use public transport.

Monitoring

Some suggested monitoring measures that relate specifically to this recommendation are as follows:

• Perform surveys of public transport passenger numbers; and

• Determine mode share of people travelling in area or city.

Case Studies

BRT system, Bogota, Colombia

Source: ESMAP (2009). “Good Practices in City Energy Efficiency: Bogota, Colombia—

Bus Rapid Transit for Urban Transport Energy,” available online at

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https://www.esmap.org/sites/esmap.org/files/CS_Bogota_020310_0.pdf

With the completion of its first two phases, the TransMilenio BRT system serves

about 1.5 million passengers every day and has reduced citywide fuel consumption by 47

percent. Key success factors have been citywide comprehensive planning of infrastructure,

use of state-of-the-art technologies, implementation of a variety of design features to

accommodate high volumes of passengers, and the use of a simple single-price fare

system. It does not require subsidies for operation—these are fully covered by fares. The

project’s capital cost totaled USD240 million. The system is managed by a company that

was set up by the mayor, but runs independently from the city administration. While the

company is in charge of all planning, maintenance, and construction of infrastructure as

well as organization of bus service schedules, buses and drivers are contracted through

private firms, resulting in a complex but innovative management structure.

Land Use and Public Transport Planning, Curitiba, Brazil

Source: World Bank (2010). “Curitiba, Brazil—Cost Is No Barrier to Ecological and

Economic Urban Planning, Development, and Management.” In ECO2 Cities: Ecological

Cities as Economic Cities, pages 169-182. Available online at

http://www.esmap.org/esmap/sites/esmap.org/files/CS_Curitiba.pdf .

The case of Curitiba, Brazil, shows that cost is no barrier to ecological and

economic urban planning, development, and management. Curitiba has developed a

sustainable urban environment through integrated urban planning. To avoid unplanned

sprawl, Curitiba directed urban growth linearly along strategic axes, along which the city

encouraged high-density commercial and residential development linked to the city’s

integrated master plan and land-use zoning. Curitiba adopted an affordable but innovative

bus system rather than expensive railways that require significant time to implement.

Curitiba’s efficient and well-designed bus system serves most of the urban area, and public

transportation (bus) ridership has reached 45 percent. The city now has less traffic

congestion, which has reduced fuel consumption and enhanced air quality. The green area

has been increased, mainly in parks that have been created to improve flood prevention

and through regulations that have enabled the transfer of development rights to preserve

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green areas and cultural heritage zones.

Linking development densities to public transport availability, Curitiba, Brazil

Source: Rabinovitch, J. (1992). “Curitiba: Towards Sustainable Urban Development,

Environment and Urbanization,” Vol. 4 (2) pp. 62-73. Available at

http://eau.sagepub.com/content/4/2/62.abstract .

Curitiba's master plan integrated transportation with land-use planning. Zoning laws

are used to direct linear growth by attracting residential and commercial density along a

mass transportation lane. High-density residential and commercial development is

permitted within walking distance of stops, with much lower densities elsewhere in the city.

The city’s central area is partly closed to vehicular traffic, and pedestrian streets have been

created. In addition, a strict street hierarchy safeguards the right of way for the current BRT,

which has significantly contributed to the success of the transportation network.

Integrated urban planning and efficient resource use, Singapore

Source: “Good Practices in City Energy Efficiency: Eco2 Cities: Land and Resource

Management in Singapore,” available online at http://www.esmap.org/esmap/node/1230 .

Singapore is an island city-state at the southern tip of the Malay Peninsula. With a

land area of 700 square kilometers and a population of 4.8 million, Singapore has become

developed because of innovative urban planning integrated with the efficient use of land

and natural resources. Singapore’s small size poses a challenge when it comes to the

availability of land and natural resources. To optimize land use, Singapore promotes high-

density development not only for businesses and commercial entities, but also for

residential structures. High density lends itself to higher economic productivity per unit of

land and facilitates the identification of green spaces and natural areas for preservation.

Furthermore, high-density development has translated into greater use of public

transportation as major business, commercial, and residential areas are well connected to

an integrated public transportation network. In 2004, public transportation as a share of all

transportation modes during morning peak hours reached 63 percent. The significant use of

public transportation helps reduce greenhouse gas emissions. High public transportation

ridership also means Singapore has been able to recover all public transportation operating

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costs from fares, a feat only also achieved by Hong Kong, China, among modern, highly

developed cities.

Integrated regional urban planning, Auckland, New Zealand

Source: “Good Practices in City Energy Efficiency: Eco2 Cities: Integrated Regional Urban

Planning in Auckland,” available online at http://www.esmap.org/esmap/node/1227 .

The interconnectedness of national and local Auckland issues (such as housing and

education) with growth and innovation, and the major required investments (particularly in

land transport) have created complex and difficult issues among multiple authorities.

Despite Auckland’s importance to the New Zealand economy and the areas of common

interest, such as transportation and energy provision, the national government did not

initially play a close role in directing regional and local government planning. Concern

emerged that, without agreement on an overarching regional strategy and framework,

decision making in the region could become ad hoc and adversarial if each stakeholder

tried to have a say from a narrow perspective and without viewing the region as a whole. As

a result, there was a clear need for coordinated strategic planning across the Auckland

region to ensure that Auckland would be able to remain competitive in today’s globalized

world. The response involved a process undertaken in 2001 to prepare a regional growth

strategy that aimed to provide a vision of what Auckland could be like in 50 years.

Tools and Guidance

Public Transport Authority Western Australia (2009). “Bus Priority Measures Principles and

Design.” A guidance document for planning bus priority methods and approaches. Available

online at http://www.pta.wa.gov.au/PublicationsandPolicies/DesignandPlanningGuidelines/tabid/

109/Default.aspx .

Transport for London (2006). “Accessible Bus Stop Design Guidance.” A guidance

document for designing bus stops that helps make boarding easier for passengers.

Available online at http://content.tfl.gov.uk/accessibile-bus-stop-design-guidance.pdf

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4.Non-Motorized Transport Modes

Description

Non-motorized transport modes have zero operational fuel consumption and require low capital costs for implementation. In addition to improving the health of users, their use reduces noise pollution and improves air quality.

Benefits include improved air quality, lower operating costs for users and providers, and lower infrastructure requirements.

Attributes

Energy Savings Potential

100,000-200,000 kWh/annum

First Cost

> USD1,000,000

Speed of Implementation

> 2 years

Co-Benefits

Reduced carbon emissions

Improved air quality

Enhanced public health and safety

Implementation Options

Implementation Activity Methodology

Pedestrianization The city authority pedestrianizes

networks of streets or larger city areas.

Either permanent or temporary, the

closure of streets to motor vehicles, or

traffic-calmed zones with speed

reducing facilities increases public

awareness of non-motorized modes

and removes noisy and polluting

vehicles, as well as creates

opportunities for street markets and

other initiatives. The city authority

researches the feasibility and probable

take-up from origin and destination

surveys, existing mode splits, and

subsequently designs networks to suit

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commuting patterns and

local/neighborhood travel. See Oxford

case study for further details.

Dedicated networks

The city authority includes dedicated

cycle/walking route networks in its

transportation or city land-use plans.

Replacement or reservation of rights-of-

way in newly built areas creates the

necessary conditions for adopting non-

motorized modes that may otherwise be

less favored if roads cater only to cars.

The key to success is the linkage of

cycle and pedestrian networks at the

local level, and the quality of the

environment provided, which requires

good drainage and adequate lighting

and shade. See Bogota case study for

further details.

Microcredits

The city authority makes available micro

credits, which can be used to increase

the ownership of bicycles. Increased

bicycle ownership can have significant

financial benefits to low-income workers

who may no longer be dependent upon

expensive, inefficient, and infrequent

public transport. See Lima case study

for further details.

Rental programs The city authority introduces bicycle

rental programs, which provide bicycles

on demand for a fee. The key factor for

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success is the setting of tariffs that

encourage use as well as security

procedures that avoid and penalize

theft. Registered-user schemes require

a user’s credit card or bank details, but

are not necessarily open to all. Non-

registered user schemes are more

flexible, but more open to abuse.

Branding of bicycles and facilities can

create revenue for the local authority.

See Paris case study for further details.

Monitoring

Some suggested monitoring measures that relate specifically to this recommendation are as follows:

• Perform surveys of the number of cycles in circulation by using traffic counters on roads and cycle lanes;

• Determine the mode share of people travelling in the area or city; and

• Determine KPIs such as percentage of non-motorized transport mode, modal shift, kilometers of dedicated cycle/walking infrastructure, take-up of cycle promotion schemes by analyzing registers of subsidies.

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Case Studies

Pedestrianization with road closures, Oxford, England, UK

Source: European Commission, Directorate General for the Environment (2004).

“Reclaiming City Streets for People: Chaos or Quality of Life?” available online at

http://ec.europa.eu/environment/pubs/pdf/streets_people.pdf .

The main retail streets have been fully pedestrianized, while other through roads in

the central area are only accessible to buses and pedestrians. The adoption of a step-by-

step, integrated approach to the implementation of the road closure program has been

seen as critical to the success of the significant road-space reallocation element of the

scheme. Opposition to the USD6 million scheme was raised most notably on the grounds

that traffic congestion on two key routes in the city would worsen, as well as from retailers

concerned about delivery access and trade levels. These concerns were attended to via an

extensive consultation process and an effective publicity campaign prior to the

implementation of the scheme. This included leaflets, advertisements on buses, citywide

poster boards, and a series of press releases.

Dedicated cycle network, Bogota, Colombia

Source: C40 Cities (2010). “Bogota, Colombia: Bogota's Ciclorutas is one of the most

comprehensive cycling systems in the world,” available online at

http://www.c40cities.org/bestpractices/transport/bogota_cycling.jsp

Ciclorutas is considered a unique cycling network where design has taken the

topography of the city into consideration in order to create maximum flow and function

(manmade and natural features, hills, waterways, parklands, essential facilities). In a period

of just seven years, following an investment of USD50 million, the use of bicycles on the

network increased by more than 268 percent. Ciclorutas plays an important role for lower-

income groups as more than 23 percent of the trips made by the lowest-income group in

the city are by walking or by bicycle. The development of Ciclorutas has also helped

recover public space along riverbanks and wetlands as for many years the city’s wetlands

were occupied by illegal settlements.

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Bicycle micro credits, Lima, Peru

Source: ICLEI (2009). “Case Study 46: Assistance to Purchase Bicycles—Lima, Peru” in

“Sustainable Urban Energy Planning: A Handbook for Cities and Towns in Developing

Countries,” available online at http://www.unhabitat.org/pmss/listItemDetails.aspx?

publicationID=2839

In 1990, the Municipality of Lima set up a micro-credit program to help low-income

citizens purchase bicycles. By saving on daily public transportation costs, workers can see

their income effectively rise more than 12 percent once the loan is paid off. In order to

enhance the success of the program, efforts have been made at standardizing the use of

bicycles in the city. Actions to achieve this have so far consisted of the development of a

manual of technical standards for the design and planning of cycle ways.

Bicycle rental, Vélib’, Paris, France

Source: C40 Cities (2011). “Velib - A New Paris Love Affair,” available online at

http://www.c40.org/case_studies/velib-%E2%80%93-a-new-paris-love-affair

Paris launched a 24/7 bicycle hire scheme through Vélib’, a public-private

partnership between the City of Paris and a company led by a major advertising group.

Users must purchase a daily, weekly, or annual subscription and bike rental is free for the

first half hour of every individual trip after which it costs a fixed rate. The escalating price

scale ensures that the bikes are kept in circulation. Notably, the City of Paris generates

revenues from the project without any investment (which cost USD108 million). The public-

private partnership is the reason for this success, with the private company paying

operating costs plus rights to advertising space to the city funded by advertising revenues.

Tools and Guidance

Sustrans (2007). “Technical Guidelines for the Development of Cycle Facilities.” A series of

guidance documents for professionals on the details of bicycle network design. Available

online at http://www.sustrans.org.uk/resources/design-and-construction/technical-guidelines .

Transport for London (2014). “London Cycling Design Standards.” A guidance document for

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designing to reduce barriers to cycling in order to support road safety targets. Available

online at:https://consultations.tfl.gov.uk/cycling/draft-london-cycling-design-standards/

user_uploads/draft-lcds---all-chapters.pdf

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5.Parking Restraint Measures

Description

Restricting parking availability discourages car use and provides an incentive to use more sustainable modes of transport, including public transport.

Removing vehicles from circulation reduces fuel use and the effects of congestion.

Attributes

Energy Savings Potential

100,000-200,000 kWh/annum

First Cost

< USD100,000

Speed of Implementation

> 2 years

Co-Benefits

Reduced carbon emissions

Improved air quality

Enhanced public health and safety

Increased employment opportunities

Implementation Options

Implementation Activity Methodology

Planning measures The city authority introduces planning

measures, which determine car-parking

provision for residential and office

developments. Introducing maximum

parking allowances with low car-to-unit

ratios discourages private-car acquisition

and use. Such measures do not affect

the existing parking provision, however,

and so need to be supported by

additional measures. While areas of

intervention can be defined, larger

coverage is more effective as it has less

potential to overwhelm surrounding

areas. A gradient approach solves this by

making requirements less stringent from

the center to the periphery. These

measures safeguard energy use and

efficiency in design and thereby bear no

immediate cost to the city authority. See

London case study for further details.

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Parking fees

The city authority set systematic

hierarchical charging scheme for on

street as well as off-street parking.

Implementing a charging regime for car

parking and formalizing parking

arrangements will enable the parking

stock to be controlled and generate a

revenue stream for sustainable transport

measures. This type of approach

requires a supporting system for

enforcement, e.g., traffic wardens who

issue fines to violators, and are politically

sensitive measures. See London and

San Francisco case study for further

details.

Park & Ride facilities

The city authority promotes multimodality

by providing Park & Ride locations at key

interchanges. By linking parking to public

transport use, the necessities of non-

inner city residents are considered. The

success of Park & Ride is linked to

availability of public transport and

unavailability of cheap parking in central

locations. The perceived cost should be

lower than that of driving the entire way.

Measures of this kind often require major

capital investment in infrastructure by the

city authority with respect to Park & Ride

locations on the periphery of the city, bus

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terminals, and additional buses. See

Oxford case study for further details.

Complementary implementation activity:

Planning measures

Monitoring

Some suggested measures that relate specifically to this recommendation are as follows:

• Perform surveys of parking stock and usage;

• Perform traffic surveys of number of vehicles in circulation by using traffic counters;

• Determine the average travel speeds on the main transport corridors;

• Determine the mode share of people travelling in the area or city; and

• Perform statistical analysis of rate of growth of car registration data.

Case Studies

Parking standards, The London Plan, London, UK

Source: London (2010). “Chapter 6: Transport” in The London Plan, available at

http://www.london.gov.uk/shaping-london/london-plan/docs/chapter6.pdf pp.160-161.

The London Plan establishes maximum parking guidelines for residential

development. It stipulates that all development in areas of good public transport

accessibility should aim for significantly less than one parking space per unit. The main

challenge continues to be ensuring that these standards are supported by other measures

that reduce car dependency, both within the development and in the surrounding area, e.g.,

improved and increased public transportation accessibility.

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SFpark curbside parking, San Francisco, California, USA

Source: The Institute for Transportation and Development Policy (2010). “U.S. Parking

Policies: An Overview of Management Strategies,” available online at

https://www.itdp.org/wp-content/uploads/2014/07/ITDP_US_Parking_Report.pdf

San Francisco Municipal Transit Agency (SFMTA) installed new electronic, multi-

space meters in 2009 and activated parking spot sensors attached to the pavement in

2010. The aim is to use pricing to help redistribute the demand for parking. At the heart of

SFpark is a data management system that sorts a tremendous amount of data collected

from the networked array of remote sensors in all 6,000 parking spots. These wireless

sensors can detect whether a spot is occupied by a vehicle and report parking occupancy

information in real time to a central computer. The project produced valuable data about the

effect of meter pricing on occupancy. Drivers can check the available parking spots via

SFPark website, as well as smartphone app. The system took effect in April 2011,

compassed 6,000 of San Francisco’s 25,000 metered curbside parking spots in seven pilot

neighborhoods and additional fourteen city-owned garages. A March 2014 study found that

SFPark met its 60-80% occupancy goal and that cruising for parking is down by 50%.

Parking fees, Aspen, Colorado, USA

Source: The Victoria Transport Policy Institute (2010). “Parking Pricing Implementation

Guidelines,” available online at http://www.vtpi.org/parkpricing.pdf .

The city used to suffer from high levels of congested on-street parking. In order to

reduce the effects of the “90-minute shuffle” (where locals and downtown commuters

moved their vehicles every 90 minutes to avoid getting a parking ticket), the city introduced

charges for on-street parking using multi-space meters. Parking fees are highest in the

center and decline with distance from the core. The city had a marketing campaign to let

motorists know about the meters, including distribution of one free prepaid parking meter

card to each resident to help familiarize him or her with the system. Motorists were allowed

one free parking violation, and parking control officers provide an hour of free parking to

drivers confused by the meters.

Park-and-Ride, Oxford, England, UK

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Source: Oxford City Council (2009). “Park and Ride Transfer,” available online at

http://www.oxford.gov.uk/PageRender/decTS/Park_and_Ride_occw.htm .

Oxford city has five Park-and-Ride sites serving the city’s shoppers, visitors, and

commuters. These sites used to charge for parking to provide income to cover operational

costs, but were not able to generate additional revenue for repairs or improvement. In order

to achieve savings, the management of the Park-and-Ride sites was transferred to

Oxfordshire county, resulting in efficiency savings of GBP250,000 per year for the city

administration. These savings were achieved primarily through economies of scale, and by

sharing the cost of providing the service with taxpayers across the county, and not just

those in the city—both of whom used the facilities.

Tools and Guidance

The Victoria Transport Policy Institute (2010). “Parking Management: Strategies, Evaluation

and Planning.” A comprehensive guidance document for planning and implementation of

parking management strategies. Available online at http://www.vtpi.org/park_man.pdf .

The Victoria Transport Policy Institute (2010). “Parking Pricing Implementation Guidelines.”

A guidance document for implementation of parking pricing with details on overcoming

common obstacles. Available online at http://www.vtpi.org/parkpricing.pdf

Spillar, R. (1997). “Park-and-Ride Planning and Design Guidelines.” A guidance document

for the planning and design of Park-and-Ride facilities. Available online at

https://www.pbworld.com/pdfs/publications/monographs/spillar.pdf

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6.Traffic Restraint Measures

Description

Discouraging potential drivers from using their cars leads to fewer cars in circulation. This encourages people to use alternative modes, which in turn will increase their viability (increased public transport patronage, for example).

Removing vehicles from circulation reduces fuel use and the need for road space.

Attributes

Energy Savings Potential

100,000-200,000 kWh/annum

First Cost

USD100,000-1,000,000

Speed of Implementation

1-2 years

Co-Benefits

Reduced carbon emissions

Improved air quality

Enhanced public health and safety

Implementation Options

Implementation Activity Methodology

Blanket bans

The city authority imposes blanket

bans. Possible types of blanket bans

include vehicle-type bans that exclude

entire vehicle categories from

circulation; or license plate bans, by

which certain number plates are banned

from circulation. A weakness of license

plate bans is that they tend to result in

wealthier residents purchasing second

cars, not only negating the aims of the

ban, but thereby also disadvantaging

those with lower incomes. See

Guangzhou case study for further

details.

Licensing

The city authority rations permits. The

establishment of quotas for private

vehicles allows for only a certain

number of vehicle registrations over a

given period of time. However, as the

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demand for cars tends to be inelastic,

this often results in very high purchase

prices for the licenses—a mechanism

which favors the wealthy and

marginalizes the lower-income brackets

of society. See Singapore case study

for further details.

Civic initiatives

The city authority sanctions and

encourages “no-driving days” to

educate and lead by example.

Participation in these initiatives is

voluntary, however, and therefore not

enforceable. See Puerto Princesa case

study for further details.

Monitoring

Some suggested monitoring measures that relate specifically to this recommendation are as follows:

Perform traffic surveys of the number of vehicles in circulation pre- and post-implementation;

Determine the mode share of people travelling in an area or the city; Collate registration data of users to paid schemes or voluntary schemes; and Perform statistical analysis of rate of growth of car registration data.

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Case Studies

Vehicle bans: Motorcycle ban, Guangzhou, China

Source: The Institute for Transportation and Development Policy (2008). “Motorcycles Ban

in Guangzhou,” available online at

http://s3.itdp-china.org/docs/Motorcycle+ban+in+Guangzhou+-+Sep-08.pdf

Motorcycles have been completely banned in the City of Guangzhou. The ban was

implemented in phases, beginning with a moratorium on new licenses, extending to various

roads and time periods. Gradual implementation has been crucial to allow time for the

public to adapt, and efficient supply of additional infrastructure/services has supported the

induced modal shift. Many motorbike riders have shifted to bicycles and buses, and cycle

rickshaws have also emerged as a popular substitute. Road accidents have dropped by 40

percent since the ban was implemented from 2004

Rationing, Singapore, Singapore

Source: Sustainable Urban Transport Project (2010).”The Vehicle Quota System in

Singapore,” available online at

http://www.sutp.org/files/contents/sutp-archive/documents/NL-Apr-May-09.pdf

Singapore sets the number of new vehicles allowed for registration. Potential buyers

need to bid for a non-transferable license, which entitles them to own a vehicle for a fixed

number of years. The scheme had to be modified soon after implementation to safeguard

against speculative action. The licenses used to be transferable and within the first two

months of the first round of release 20 percent changed hands in “buy and sell”

transactions with speculators making sizable profits of up to SD5,000. As the rationing

system does not control annual mileage, the success of the rationed registration in limiting

vehicle usage has been dependent on support from other traffic-restraint measures, such

as high road tolls, parking fees, and electronic road pricing.

No-driving days, One Day Rest, Puerto Princesa, Philippines

Source: ICLEI (2001). “Vehicular Reduction Strategy for Air Pollution Prevention and

Climate Change Mitigation; A Case of Puerto Princesa City, Philippines,” available online at

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http://www.iclei.org/index.php?id=1193 .

Introduced as part of a zoning and rerouting, this program stipulates a one-day rest

for tricycle drivers in the central business district. Regulation of illegally operated tricycles is

a major impediment as enforcement irregularities pose questions of inequality between

illegal and legal tricycle taxi drivers. Furthermore, the income potential of those who comply

with the rest day is lost to the illegal operators.

Tools and Guidance

Sierra Club of Canada (2001). “How to Stage a Car Free Day In Your Community.” A

guidance document for preparing and planning a community-driven car free day. Available

online at http://www.worldcarfree.net/wcfd/documents/cfd_howto.pdf .

7.Congestion Charging

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Description

Congestion charging restrains access by selected vehicle types, usually the private car, into large urban areas during congested times of the day. Usually the aim is to discourage work-based commuting trips into a defined urban area. Measures range from complete restriction to discouragement through charging. It is a market-based mechanism for influencing driver behavior, which looks to capture the “external cost” of vehicle travel during congested periods of the day.

The main benefit is realized by reducing the volume of low-occupancy vehicles entering the defined area. The aim is to induce modal transfer from low- to high-occupancy transport units, such as public transport. Maximum energy efficiency will be realized if there are complementary interventions on the public transport systems such as the implementation of energy-efficient vehicles. Congestion charging should provide a revenue stream with the surplus (after operating costs) invested in transport systems that are more efficient.

Attributes

Energy Savings Potential

100,000-200,000 kWh/annum

First Cost

> USD1,000,000

Speed of Implementation

> 2 years

Co-Benefits

Reduced carbon emissions

Improved air quality

Enhanced public health and safety

Implementation Options

Implementation Activity Methodology

Congestion pricing

The city authority introduces congestion

charging. The key to effective

congestion relief is the price setting.

Most effective systems will operate with

a simple pricing structure although in

practice it is likely that this will be

difficult to achieve. Vehicles would be

charged for entering a defined zone

with the charge generally levied through

the purchase of permits, in the case of

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congestion charging, or by conventional

charging for toll roads, either by using

automatic collection by means of signal-

controlled devices or manually. Physical

restriction of selected vehicles into a

zone seeks to target a group that can

vary by type or time of day/week/year.

Implementation requires measures to

be in place supported by legislation to

enable adequate enforcement. These

types of measures raise revenue that

can be invested in other public

infrastructure. See London, Singapore,

and Stockholm case studies for further

details.

Monitoring

Some suggested measures that relate specifically to this recommendation are as follows:

• Perform traffic surveys of the number of vehicles in circulation pre- and post-implementation;

• Determine the mode share of people travelling in an area or the city;

• Collate registration data of users to paid schemes or voluntary schemes; and

• Perform statistical analysis of rate of growth of car registration data.

Case Studies

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Congestion charge, Stockholm, Sweden

Source: C40 Cities (2010). "Stockholm: Congestion Charge," available online at

http://www.c40cities.org/bestpractices/transport/stockholm_congestion.jsp .

Drivers are charged every time upon entry into and out of the congestion zone

(“crossing the cordon”), which encompasses the city center. The charge varies according to

the time of entry, and high-definition cameras with Automated Number Plate Recognition

software are used to register vehicles. Drivers are automatically billed, usually by 7 p.m. the

same day. Measures that have been key to addressing the perceived implementation

barriers have been a simple and user-friendly zone charging structure; a simplified payment

process; and a consideration of seasonal traffic variations to enhance public opinion (the

month of July—a key holiday in Sweden—is exempt from the charge).

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Congestion charge, London, UK

(1) Source: ESMAP (2011). “Good Practices in City Energy Efficiency, London, UK:

Congestion Charges for Urban Transport,” available online at

http://www.esmap.org/esmap/node/1279 .

In February 2003, London, the capital city of the United Kingdom, introduced a daily

congestion fee for vehicles travelling in the city’s central district during weekdays. This fee

was meant to ease traffic congestion, improve travel time and reliability, and make Central

London more attractive to businesses and visitors.

According to analysis by the city, the program has largely met its objectives. After

four years of operation, traffic entering the charge zone was reduced by 21 percent;

congestion, measured as a travel rate (minutes per kilometer), was 8 percent lower; and

annual fuel consumption fell by approximately 44-48 million liters or about 3 percent. 

These changes translated into 110,000-120,000 tons of carbon dioxide (CO2) reductions

annually, a 112 ton reduction in nitrogen oxides (NOx), an eight-ton reduction in particulate

matter (PM10), and some 250 fewer accidents. 

In terms of the program cost-effectiveness, the identified benefits exceeded the

costs by more than 50 percent.  In addition, the scheme brought a steady net revenue

stream for transport improvements, of which 80 percent has been reinvested in improving

public bus operations and infrastructure.  

Among the first programs of its kind, London’s congestion charging scheme was

successfully developed and implemented.  The city proved to be innovative and resourceful

by ensuring key elements of the scheme were in place, including technical design, public

consultation, project management, information campaign, and impact monitoring.  London’s

innovation has helped other cities around the world assess this as a policy option in

meeting their urban transport needs.

(2) Source: UN Habitat (2006). “London's Congestion Charging System,” Habitat

Debate, Vol. 12, No. 1, available online at

http://ww2.unhabitat.org/HD/hdv12n1/Vol12No1e.pdf .

The London USD170,000,000 congestion charge scheme uses a flat-rate fee

applicable during normal working hours on weekdays as it is both easy to understand and

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implement, and is also reflective of the nature of congestion in London (consistent

throughout the day). Video cameras at entry points to the zone and mobile units within the

zone register vehicles that enter the zone by means of automatic number plate recognition

technology. Payments are made electronically on the day of entry into the zone. There are

discounts for monthly/annual payments, as well as 90 percent discounts for residents within

the priced area.

As a measure to meet the predicted rise in demand for public transportation, the city

authority invested in the pre-implementation expansion of the bus service. Results show

that the scheme has reduced congestion in the central zone by 18 percent; reduced delays

by 30 percent; and caused major reductions in road accidents (70 less per annum). Surplus

revenue over operating costs for the original zone are used to improve the efficiency of

public transport systems. The city authority is now looking to expand the scheme at a

forecast cost of USD25 million to USD40 million for the zone extension.

Congestion charge, Singapore, Singapore

Source: Singapore Land Transport Authority (2002). “Road Pricing—Singapore’s

Experience,” available online at http://citeseerx.ist.psu.edu/viewdoc/download?

doi=10.1.1.128.8783&rep=rep1&type=pdf

Implemented first in 1975, Singapore’s congestion pricing initiative has evolved from

a manual scheme based on paper permits and applicable only during the morning peak

period to an electronic version that operates throughout the day. The city authority enacted

a pre-implementation expansion of the bus fleet to meet the predicted rise in demand and

also developed new Park-and-Ride facilities to support the scheme. Results show that

weekday traffic entering the restricted zone has been reduced by 24 percent (271,000 to

206,000 vehicles/day). Annual revenue is approximately 11 times the initial capital costs

and annual running costs, giving a significant payback. However, the variable cost of entry

into the restricted zone has made the scheme difficult to enforce.

Tools and Guidance

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US Department of Transportation (2009). “Value Pricing Pilot Program Planning and

Decision Making Tools,” a series of tools for estimating the impact of congestion pricing

strategies. Available online at http://ops.fhwa.dot.gov/congestionpricing/value_pricing/tools/

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8.Travel Planning

Description

Informing drivers about alternative modes of transport and sharing resources with other drivers leads to fewer cars being used and more trips with public transport.

Removing vehicles from circulation reduces fuel use and increases the viability and efficiency of public transport.

Attributes

Energy Savings Potential

100,000-200,000 kWh/annum

First Cost

USD100,000-1,000,000

Speed of Implementation

1-2 years

Co-Benefits

Reduced carbon emissions

Improved air quality

Financial savings

Implementation Options

Implementation Activity Methodology

Educational

Campaigns can be run to educate

drivers about alternatives to car travel,

including walking, biking, public

transportation or carpool options. Once

a target population is identified, it is

provided with promotional material of

sufficient detail such as maps,

brochures, and tips, as well as

invitations to attend community events.

See Portland case study for more

details.

Information

dissemination

Travel plans seek a commitment from a

group of users to create and implement

a strategy to reduce car use and

increase use of alternative travel

modes.

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Economic

Car clubs are an initiative to share a

carpool among a group of users,

maximizing the utility of the carpool by

reducing idle time. Members do not own

the club’s cars, but can order and use

one for a fee. The price incentive lies in

the withdrawal of personal responsibility

over the running costs of the fleet, with

insurance and maintenance costs being

included in the membership package.

Monitoring

Some suggested monitoring measures that relate specifically to this recommendation are

as follows:

• Perform traffic surveys of number of vehicles in circulation by using traffic counters;

• Determine mode share of people travelling in an area or city; and

• Perform statistical analysis of registration data of users to paid schemes or voluntary

schemes.

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Case Studies

Driver Education, SmartTrips, Portland, USA

Source: SmartTrips Newsletters #1 (2015), “Welcome to Portland SmartTrips”, available

online at https://www.portlandoregon.gov/transportation/article/535740

Run by the city’s Office of Transportation, SmartTrips is a campaign that aims to inform

Portland’s citizens of the various existing alternatives to single-occupancy vehicle trips. It

hand delivers information packets to residents, detailing available alternative modes of

transportation, and distributes supporting maps and information on relevant event

schedules. The SmartTrips campaign operates by targeting specific areas and different

target groups over its lifetime, and notably runs “Senior Strolls,” which are slower paced

walks that help seniors become active and comfortable with walking as a transportation

option, as well as “Women’s Clinics,” which educate women on how to ride with children

and how to shop by bike. The program is funded by revenues from the city’s share of gas

taxes and other transportation revenues, supplemented by energy tax credits earned by

private businesses.

Travel plans, Nottingham Hospital, Nottingham, United Kingdom

Source: Rye, T. (2002) “Travel Plans: Do They Work?” Transport Policy, Vol. 9, No. 4, pp.

287-298. http://www.sciencedirect.com/science/article/pii/S0967070X02000045

Nottingham City Hospital has approximately 14,000 two-way car trips (including

visitors, patients, and deliveries) accessing its site each day. When the hospital underwent

redevelopment and expansion work, associated planning regulated required measures to

reduce this number of car trips. The hospital management introduced a range of measures,

including improved pedestrian and cycle access to the site, staff discount at a local bicycle

shop, bus services running through the hospital site linking local estates and suburbs

(though these services receive no subsidy from the hospital), and increased transport

information on the intra- and Internet sites. The results were reductions in single-occupancy

vehicle trips with significant increases in ride sharing and use of public transportation.

Observations have been made that expanding the ride-share scheme to other local

employers could increase the number of potential matches and uptake.

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Car clubs, Singapore, Singapore

Source: Foo, T. S. (2000). “Vehicle Ownership Restraints and Car Sharing in Singapore."

Habitat International, Vol. 24, No. 1, pp. 75-90.

http://www.sciencedirect.com/science/article/pii/S0197397599000302

Operated by NTUC Income Co-operative, Singapore’s first residential car club is

seen as a more efficient option than individual car ownership, as individuals are able to

choose the most cost-effective mode for specific journeys. Private car ownership is very

expensive in Singapore as a result of licensing quotas, and the car club has been able to

ease the pressure on demand. The car co-operative in Singapore has also caused a net

reduction in public transport use, although a reduction in public transport use for social and

shopping trips has partly been compensated by an increase in use for commuting, reducing

congestion.

Tools and Guidance

Sustrans travel plan guidance: http://www.sustrans.org.uk/what-we-do/active-travel/active-

travel-information-resources/active-commuting-and-travel-plans-help-and-advice/active-

commuting-and-travel-plans-good-practice .

Aukland Sustainable Transport Plan (2006). Available online at

https://at.govt.nz/media/imported/4827/AT_ARTA_Policy_SustainableTransportPlan2006_1

6.pdf

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9.Awareness-Raising Campaigns

Description

Public education and training campaigns will increase the public’s awareness and understanding of the benefits of energy efficiency and can help change attitudes towards energy efficiency. Providing information on easy ways to be more energy efficient can help modify citizen behavior and contribute to overall energy savings. This can be achieved through:

Advertisement campaigns; Public events; Articles in the local press; User-friendly website providing information about

energy efficiency; Training programs in schools, community centers, and

businesses; and An “energy efficiency champion” program.

Key benefits are more efficient energy behaviors by residents leading to reduced energy consumption within the city. Indirect benefits include reduced pressure on energy infrastructure, reduced carbon emissions, and better air quality.

Attributes

Energy Savings Potential

100,000-200,000 kWh/annum

First Cost

USD100,000-1,000,000

Speed of Implementation

< 1 year

Co-Benefits

Reduced carbon emissions

Improved air quality

Enhanced public health and safety

Financial savings

Security of supply

Implementation Options

Implementation Activity Methodology

Targeted training

programs

Working with an experienced

education/training provider, the city

authority develops training programs

that can be rolled out in schools and

offices. These programs should target

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big energy users, for example, offices.

These programs can also be

implemented through a partnership with

other organizations such as utility

companies, businesses, and NGOs.

Public education

campaigns

Working with an advertising and

marketing company experienced in

public education campaigns, the city

authority develops a strategy for

providing information on energy

efficiency to all residents. This can

include posters, billboards, and leaflets,

as well as public media announcements

and advertisements. A partnership can

be created with a business or utility

company to help finance this.

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Energy efficiency

champions

The city authority recruits local energy

efficiency champions and trains them to

teach people about the importance and

benefits of energy efficiency.

Champions can be anyone interested in

spreading the message about energy

efficiency, for example, local authorities,

businesses, local community groups,

NGOs, health trusts, school children,

and other individuals. This

implementation activity can be carried

out in a number of ways:

• Ask champions to come to a

“train the trainer” course and

provide them with support to run

sessions within their own

community.

• Teach champions about simple

ways to save energy and then

give them leaflets to distribute in

their community. Ensure that

champions inform people that

they are the local contact for any

energy efficiency questions.

Since energy efficiency champions are

often volunteers, an officer should be

appointed to provide support and

encouragement, conduct regular follow-

ups and monitor progress of each

energy efficiency champion program.

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Monitoring

Some suggested monitoring measures that relate specifically to this recommendation are as follows:

• Number of people participating in training programs annually;

• Number of hits to city energy efficiency website monthly (if developed) or number of requests for energy efficiency measures;

• Number of articles in the press about energy efficiency in the city; and

• Number of energy efficiency champions trained (if this option is chosen).

Case Studies

PlaNYC, New York, New York, USA

Source: PlaNYC. Available online at

http://www.nyc.gov/html/planyc/html/home/home.shtml

PlaNYC is a comprehensive sustainability plan for New York City’s future. The plan

puts forth a strategy to reduce the city’s greenhouse gas footprint, while also

accommodating a population growth of nearly one million, and improving infrastructure and

the environment. Recognizing the importance to reduce global carbon emissions, and the

value of leading by example, New York has reduced its citywide carbon emissions by 19

percent since 2005, and it is on track to reach the reduction of 80 percent by 2050.

Within the energy sector of the plan, the city has an initiative to undertake extensive

education, training, and quality control programs to promote energy efficiency. In 2010, the

city launched an energy awareness campaign and set up training, certification, and

monitoring programs. The plan proposes that these measures will be delivered through a

series of partnerships until an Energy Efficiency Authority is established.

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Energy Efficiency Office, Toronto, Canada

Source: City of Toronto. Available online at http://www.toronto.ca/energy/saving_tips.htm .

The Energy Efficiency Office in Toronto provides energy saving tips for households,

businesses, and developers on the city’s website. As an example, the Energy Efficiency

Office conducts the Employee Energy Efficiency at Work (E3@Work), an awareness

program designed to save money and promote energy efficiency practices by managing

office equipment power loads. Developed and implemented by the City of Toronto in 2002,

the program is being promoted to business establishments and offices across the city. The

goal is to reduce energy consumption and building operating costs, improve energy security

and reliability, and help preserve the environment.

Low Carbon Singapore, Singapore

Source: Low Carbon Singapore. Available online at http://www.lowcarbonsg.com .

“Low Carbon Singapore” is an online community dedicated to help Singapore

reduce its carbon emissions and move towards the goal of a low-carbon economy. The

project aims to educate individuals, communities, businesses, and organizations on issues

relating to climate change, global warming, and clean energy, providing information, news,

tips, and resources on various ways to reduce carbon emissions, including adoption of

clean energy and energy efficient behaviors and technologies.

Low Carbon Singapore is published by Green Future Solutions, a Singapore-based

business that promotes environmental awareness and action for a green future through a

network of green websites, events, presentations, publications, and consultancy.

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Carbon Management Energy Efficiency (CMEE) Program, Walsall Council, UK

Source: Walsall Council. Available online at

http://www.walsall.gov.uk/index/energy_awareness_staff_presentations.htm .

Walsall Council has been rolling out energy awareness training with the Carbon

Trust under their funded Carbon Management Energy Efficiency (CMEE) program,

including:

• Energy surveys of the council’s least energy efficient buildings;

• Evaluating feasibility of combined heat and power (CHP) generation at the council’s

leisure centers; and

• Raising staff awareness through a number of energy presentations to senior

managers, building managers, school caretakers, and a number of the council’s

general staff. A total of 226 staff were trained in this round using presentations

developed by the Carbon Trust and adapted, with the help of some of the

environmental champions, to reflect Walsall Council’s needs.

The aim of the CMEE program is to identify and achieve significant carbon savings

throughout the council and, as a consequence, financial savings, too. By reducing the

energy spent, the council will also reduce the number of carbon credits it has to buy under

the Carbon Reduction Commitment, which was adopted in March 2010.

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Siemens Australia and New Zealand, Energy Efficiency Incentives

Source: Siemens. Available online at http://www.siemens.com.au/eeincentives

The Siemens Energy Efficiency Academy brings together some of the leading

international and local experts to share their insights on government policy, emerging

technologies, market drivers, and best practice implementation.

Apart from adopting and showcasing its own energy efficient practices, it runs

regular training programs for businesses across topics such as:

• Incentive schemes: Market mechanisms, grants, and funding explained;

• Building winning business cases for energy efficiency;

• Energy efficiency policy in Australian governments;

• Next generation technology: What’s next?

• Best practice implementation for variable speed drives and power quality; and

• Energy monitoring in industrial and commercial facilities.

Energy Awareness Week, Meath, Ireland

Source: ManagEnergy “EU Local Energy Action: Good Practices 2005.” Available online at

http://www.managenergy.net/download/gp2005.pdf .

In 2004, the Meath Energy Management Agency (MEMA) extended its Energy

Awareness Week to everyone who lived or worked in the County of Meath, Ireland, using a

concentrated burst of media campaigning to raise energy awareness among consumers.

Visits to schools, information displays, widespread media coverage, competitions, a “Car-

Free Day,” and an offer of free CFL light bulbs encouraged participation at all levels. The

campaign dramatically increased requests for information from the energy agency. The

competitions and promotions also improved local knowledge of energy efficiency, and

encouraged people to choose sustainable energy and transport options in the future.

Energy Awareness Week activities were coordinated and carried out by MEMA with

the support of the Environment Department of Meath County Council. The direct costs for

the campaign were USD4,470. This covered printing and copying of promotional materials,

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prizes, and provision of reflective jackets for walking bus23 participants. Local companies

and Sustainable Energy Ireland (SEI) provided additional prizes and sponsorship.

Tools and Guidance

“EU Local Energy Action: Good Practices 2005.” Available online at

http://www.managenergy.net/download/gp2005.pdf .

23 Walking Bus, is a form of student transport for schoolchildren who, supervised by two adults (a "Driver" leads and a "conductor" follows), walk to school, in much the same way a school bus would drive them to school. Like a traditional bus, walking buses have a fixed route with designated "bus stops" and "pick up times" in which they pick up children.

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Annex 2: List of City Abbreviations for Cities in the TRACE Database

City Country Abbreviation City Country Abbreviations

1 Addis Ababa Ethiopia ADD 40 Karachi Pakistan KAR

2 Amman Jordan AMM 41 Kathmandu Nepal KAT

3 Baku Azerbaijan BAK 42 Kiev Ukraine KIE

4 Bangkok Thailand BAN 43 Kuala Lumpur

Malaysia KUA

5 Belgrade Serbia BEL 44 Lima Peru LIM

6 Belo Horizonte Brazil BE1 45 Ljubljana Slovenia LJU

7 Bengaluru India BEN 46 Mexico City Mexico MEX

8 Bogotá Colombia BOG/BO1 47 Mumbai India MUM

9 Bhopal India BHO 48 Mysore India MYS

10 Bratislava Slovakia BRA 49 New York USA NEW

11 Brasov Romania BR1/BRA 50 Odessa Ukraine ODE

12 Bucharest Romania BUC 51 Paris France PAR

13 Budapest Hungary BUD 52 Patna India PAT

14 Cairo Egypt CAI 53 Phnom Penh

Cambodia PHN

15 Cape Town South Africa

CAP 54 Ploiești Romania PLO

16 Casablanca Morocco CAS 55 Pokhara Nepal POK

17 Cebu Philippines CEB 56 Porto Portugal POR

18 Cluj-Napoca Romania CLU 57 Pune India PUN

19 Colombo Sri Lanka COL 58 Puebla Mexico PUE

20 Constanta Romania CON 59 Quezon City Philippines QUE

21 Craiova Romania CRA 60 Rio de Janeiro

Brazil RIO

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22 Dakar Senegal DAK 61 Sangli India SAN

23 Danang Vietnam DAN 62 Sarajevo Bosnia and Herzegovina

SAR

24 Dhaka Bangladesh DHA 63 Seoul South Korea SEO

25 Gaziantep Turkey GAZ 64 Shanghai China SHA

26 Guangzhou China GUA 65 Singapore Singapore SIN

27 Guntur India GUN 66 Sofia Bulgaria SOF

28 Hanoi Vietnam HAN 67 Surabaya Indonesia SUR

29 Helsinki Finland HEL 68 Sydney Australia SYD

30 Ho Chi Minh Vietnam HO 69 Tallinn Estonia TAL

31 Hong Kong China HON 70 Tbilisi Georgia TBI

32 Iasi Romania IAS 71 Tehran Iran TEH

33 Indore India IND 72 Timișoara Romania TIM

34 Jabalpur India JAB 73 Tokyo Japan TOK

35 Jakarta Indonesia JAK 74 Toronto Canada TOR

36 Jeddah Saudi Arabia

JED 75 Urumqi China URU

37 Johannesburg South Africa

JOH 76 Vijayawada India VIJ

38 Kanpur India KAN 77 Yerevan Armenia YER

39 Leon Mexico LEO

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