Driving Change

Travel in the Twenty-First Century

David Metz

• Publisher: Agenda Publishing
• Year: 2019
• ISBN:
  9781788212564
• Topic: Business
• Subtopic: Infrastructure
• Index: Business

Drawing on comparative detail from Europe, North America, and the rest of the world, Driving Change provides a nuanced overview of the UK's modern transport system and the role of business models and policy choices in its evolution. The common features of mobility and travel in developed economies are highlighted in order to provide a balanced appraisal of possible future developments.

The book offers a detailed consideration of the potential of new technologies – electric propulsion, digital platforms and autonomous vehicles – to offer solutions to the intractable challenges that accompany high levels of car ownership, as well as their likely impact on business and transport policy.

Driving Change is a rich analysis of the modern state of transportation and will be welcomed by students of transport studies and policy professionals tasked with developing infrastructure and the growth of the transportation industry.

PART I

TRANSPORT LEGACY

Our modern transport system has developed over the past 200 years. Enormous investment in infrastructure has changed the landscape, both the roads and railways themselves, and the growth of towns and cities they made possible. All these structures have long lives, and most of the corridors are effectively permanent. The transport system and the travel it permits have shaped our lives and enlarged our horizons.

Yet potentially substantial changes are underway in why and how we travel. These began at the end of the twentieth century and are destined to continue. We are seeing important developments in attitudes towards the car; in size, age and location of populations; and in new technologies, both transport and wider digital. So the future of travel and transport could be very different from the past.

I start Part 1 with a review of the transport system as it is at present and the travel behaviour that has resulted from it. I then discuss how the present situation has developed. The focus of the analysis will be on travel and transport in Britain, both because its travel and transport statistics are world-leading in scope and extent, and because interpretation of such data requires a deep understanding of the societal context, which is most readily gained by residence. The book will also address what is happening in other high-income countries, particularly in Europe and North America, and will note some developments elsewhere, mainly in China. While there are significant differences between countries as regards demography and governance, there are many underlying similarities in respect of travel behaviour and the influence of new technologies.

1

A SYSTEM UNDER STRESS

Travel is central to our lives: for our daily commute, getting children to school, shopping trips, social activities, holidays and the rest. For individuals, how we travel changes through our lives, becoming more varied as we reach adulthood, when we may learn to drive and as incomes increase. Decisions about where we live and work are important for how we travel. To understand how the aggregation of decisions by individuals leads to the observed behaviour of populations, our main sources are surveys of travel behaviour, of which the most important are those carried out by national governments.

The British Department for Transport first commissioned a National Travel Survey (NTS) in 1965. The survey became a regular event starting in the early 1970s, and is now carried out annually, involving 16,000 representative individuals (a different sample each year) completing travel diaries with full details of their movements for seven days. These have provided time series of travel data spanning 45 years in considerable detail. The NTS covers all modes of travel except international air, so in effect it largely records the pattern of our daily travel, the trips that take us away from home each day.

The United States Department of Transportation carries out its National Household Travel Survey less frequently. This started in 1969 and takes place at intervals of five to eight years, most recently in 2017 when 130,000 households participated, individuals logging travel for one day of the week only. Other countries that conduct national surveys include Germany, the Netherlands, Sweden, Denmark, New Zealand and South Africa. Such surveys allow us to understand how the transport system is used, as well as how uses change over time – the topic of the next chapter.

The broad picture we find for Britain is that in 2017 (the latest available data), on average people made 975 journeys a year, travelling 6,580 miles, spending 377 hours a year on the move, which is close to an hour a day.¹ These are averages for the whole population, so we expect quite wide variations to be found among individuals. Some people rarely leave home, for instance due to disability, while others commute heroic distances. Nevertheless, the average is useful for understanding the big picture, particularly because it has changed little over the past 20 years, as I will explain in the next chapter, so that the British population now has a fairly stable and settled pattern of travel.

In developed countries, the car is the dominant mode of transport, allowing convenient door-to-door travel where road space permits. In Britain in 2017, 61 per cent of all trips were made by car, accounting for 78 per cent of distance travelled (driver and passenger), with 76 per cent of households owning at least one car. Walking accounted for 26 per cent of trips (but only 3 per cent of distance); bus transport for 6 per cent of trips (5 per cent of distance); rail travel for 2 per cent of trips (8 per cent of distance); and cycling for 2 per cent of trips and 1 per cent of distance. These are national averages.

Other developed countries have different patterns of travel, reflecting different histories and geographies. The average distance travelled by car in Britain, France, Germany and Italy is similar at about 11,000 km a year, while for the US it is about 19,000 km, Canada 15,000 km and Japan 5,500 km.² Another big difference is the popularity of cycling, notably in the Netherlands, where more than a quarter of all trips are by bicycle,³ and in Denmark where cycling accounts for 17 per cent of all trips.⁴ Rail travel also varies widely between countries: within the European Union average rail usage exceeds 1,000 passenger-km per inhabitant in Germany, France, Austria, Sweden and Britain (and in Switzerland is more than twice that), whereas in other countries it is half that or less.⁵

The main purposes of travel in Britain are for shopping (19 per cent of all trips), followed by commuting (15 per cent) and education (including escorting children to school, 12 per cent). Travel on business accounts for only 3 per cent of trips, although 8 per cent of distance.⁶ Trip lengths vary with purpose, commuting trips being longest (31 minutes on average) and escorting children to school the shortest (14 minutes).

The pattern of travel varies within countries. In dense urban areas, where road space is limited and traffic congestion is prevalent, public transport, walking and cycling are important alternatives for daily travel; so in London the car is responsible for a declining share of travel, in 2016 for only 36 per cent of trips, and there has been a corresponding growth in rail travel, which offers fast and reliable journeys compared with the car on congested roads.⁷

Densely populated towns and cities mean that large numbers of people want to travel at the same time, dictated in part by social norms for working and school hours. This puts the transport system under stress and generates a number of serious problems that we would like to tackle:

• carbon emissions from transport that contribute to climate change;

• air pollution and the damage to health this causes;

• deaths and injuries from road traffic crashes;

• road traffic congestion, and crowding on railways and at airports;

• severance of communities.

Much effort, both policy and practice, is devoted to mitigating these undesirable consequences of an era of mass mobility. I will discuss each of these in turn.

Climate change

The emissions from the internal combustion engine burning oil consists mainly of carbon dioxide, a greenhouse gas that contributes to climate change, together with the oxides of nitrogen (NO_x for short) and fine particulates (tiny particles of diameter a fraction that of a human hair), both of which are of concern on account of damage to health.

Transport is responsible for about 25 per cent of all man-made greenhouse gas emissions globally. In Britain, transport is responsible for 28 per cent, with cars contributing over half of this.⁸ In the past transport has been seen as the most difficult sector in which to achieve the reductions needed to meet overall targets aimed at reducing global warming. Improved energy efficiency and switching to electricity from non-fossil fuel sources was thought to be easier for buildings and industry.

The most recent international targets for climate change were set out in the 2015 Paris Agreement: to hold the global temperature rise this century well below 2°C above pre-industrial levels and to pursue efforts to limit the temperature increase even further to 1.5°C.⁹ This was the latest stage in a process that started with the 1992 United Nations Framework Convention on Climate Change. As yet, the voluntary national targets for reducing carbon emissions fall well short of what is required.

The main approach adopted by governments has been to set regulatory targets for the vehicle manufacturers to improve fuel economy and so reduce carbon emissions. This encouraged a switch from petrol to more efficient diesel engines, which had the unintended consequence of increasing NO_x emissions (see below). The most recent and most important response of the vehicle manufacturers is the development of electric vehicles, as I will discuss in Chapter 3. Switching to electric vehicles will eliminate the tailpipe emissions of internal combustion engines, both carbon and harmful pollutants.

Air pollution

Concerns about vehicle emissions first made an impact on public policy half a century ago in Los Angeles, prompted by the smog arising from ozone in exhaust fumes. Regulations led to the introduction of the catalytic converter, which effectively dealt with the ozone problem. It was also necessary to remove lead from petrol, a toxic material that had been included to improve engine performance but which poisoned the catalyst and was itself detrimental to health.

The success of the catalytic converter, as well as of technological innovations in other sectors that reduced environmental damage, encouraged regulatory authorities to persist with this approach in the transport sector. The general experience has been that the industry objects to proposed new regulations on grounds of technical feasibility and expense, as well as competitiveness and employment concerns, but in the event has been able to comply at acceptable cost. However, the limits of this approach have recently become evident in the case of emissions from small diesel engines.

Regulation of noxious vehicle emissions are driven by recommendations arising from assessments of health effects made under the auspices of the World Health Organization (WHO).¹⁰ The European Union has adopted WHO recommendations as the basis for legal limits to the concentration in the atmosphere of NO_x and particulates. In practice, such limits have been exceeded in many cities in Europe, and the authorities, both city and national, are required to take action to reduce emissions or face legal action and possibly fines. The European Commission has referred six member states, including the UK, to the EU Court for failures to keep below limit levels for NO_x and particulates.¹¹

The problem of air quality from transport sources has been exacerbated by the difficulty that many of the vehicle manufacturers have had in designing small diesel engines that meet regulatory requirements for NO_x emissions (bigger engines, as used in larger cars, buses and trucks, incorporate a device for injecting a chemical into the exhaust that converts NO_x to harmless nitrogen and water). A general problem has been that such engines were designed to comply with the narrow range of requirements of laboratory testing of emissions, but could far exceed the required limits when driven on the road under a wide range of conditions of engine power, temperature, speed, payload and rate of acceleration (Ligterink 2017).

While permitted emissions were reduced by 85 per cent between 2000 and 2014, on-road emissions decreased by only about 40 per cent. A particularly deplorable problem was cheating by Volkswagen, which programmed its vehicles to activate the emissions controls only under laboratory testing, and which emitted up to 40 times more NO_x on the road.¹² One consequence is that the regulatory authorities are now much more focused on real-world driving outcomes, where emissions for a range of vehicle types have been found to be over six times higher than under laboratory conditions, with substantial variations between car models.¹³

As a result of these shortcomings on the part of the manufacturers, city authorities need to introduce other measures to limit transport emissions, focusing on reducing the contribution from older diesel engines. These include the possibility of charging polluting vehicles to enter city centres, in order to encourage replacement by cleaner types.¹⁴ London has introduced the T-charge (T for “toxicity”), which requires older vehicles driven in the central area to comply with minimum emission standards or pay an additional daily charge (effectively an addition to the congestion charge, see below). The T-charge will be replaced by an Ultra Low Emissions Zone that will apply from 2021 to much of London.¹⁵ Such measures are stopgaps, aimed at reducing pollutant concentrations to below legal limits until the impact of electric vehicles is felt.

One possible approach to reducing emissions from older diesel vehicles, advocated by many, is a government-funded scrappage scheme, in the form of a cash incentive to remove such vehicles from the road. The challenge is targeting to get the best value for tax payers’ money, since the most polluting vehicles are older and tend to be less used than newer vehicles. Moreover, there is limited benefit in scrapping vehicles used mainly in rural areas. One possible approach would be to take advantage of the T-charge and similar urban emission charging schemes, since the vehicles that pay the highest cumulative charges are those that make the largest contributions to poor air quality. A scrappage scheme could then take the form of a cash-back o...

Table of contents

• Cover
• Half Title
• Title Page
• Copyright Page
• Contents
• Introduction
• Part I Transport legacy
• Part II Twenty-first-century technologies
• Notes
• References
• Index