Article
citation information:
Olojede, O.A. Transport
decarbonisation in South Africa: a case for active transport. Scientific Journal of Silesian University of
Technology. Series Transport. 2021, 110,
125-142. ISSN: 0209-3324. DOI: https://doi.org/10.20858/sjsutst.2021.110.11.
Olorunfemi Ayodeji OLOJEDE[1]
TRANSPORT
DECARBONISATION IN SOUTH AFRICA: A CASE FOR ACTIVE TRANSPORT
Summary. Over two-thirds of
greenhouse gases (GHG) emissions that contribute to climate change emanate from
transport. This could double by 2050. With per capita emissions nearly twice
the global average, South Africa ranks 13th globally on GHG emissions with road
transport, directly and indirectly, accounting for 91.2% of total transport GHG
emissions. It has been projected that by 2100, up to 100% increase in the
country’s average temperature above the 20th century average rise. This
has far-reaching implications, even for the transport sector. To decarbonise
its transport sector, South Africa has committed to reducing its GHG emissions
by 34% by 2020 and 42% by 2025, respectively, through pointed strategies and
policies. However, efficient implementation of proposed measures and sufficient
funding remain daunting challenges. Thus, this paper contends that adequate
attention has not been paid to active transport in the country’s
transport decarbonisation policy implementation despite its inclusion in policy
statements. It then asserts that active transport is indispensable to
South Africa’s achievement of its transport decarbonisation goals,
especially when steps taken hitherto seem ineffective. Consequently, the right
attitudes, regulatory instruments, and policy initiatives towards the promotion
of active transport are recommended.
Keywords: GHG emissions, decarbonisation, active
transport, South Africa
1.
INTRODUCTION: THE TRANSPORT AND CLIMATE INTERFACE
Transport
accounts for about a quarter of global energy-related carbon emissions, and this
contribution is rising faster than for any other energy end-use sector. If the
present trend continues, direct transport carbon emissions could double by 2050
[1,9,23]. Transport relies overwhelmingly on oil, with over 53% of global
primary oil consumption in 2010 used to meet 94% of transport energy demand.
This makes the transport sector a key area for energy security concerns and a
major source of air pollutants such as ozone, nitrous oxides and particulates,
as well as carbon dioxide [23]. According to the Department of Transport [21],
the overwhelming consensus of scientific opinion is that climate change in the
form of global warming is real and driven by emissions of greenhouse gases
caused by human activity. The single most important greenhouse gas (GHG) is
carbon dioxide, which as well is the single most problematic GHG source majorly
emitting from the production and consumption of fossil fuels. Meanwhile, more than
two-thirds of transport-related GHG emissions are from road transport.
Therefore, motorised transport emissions have become a significant contributor
to the global problem of GHG emissions that lead to climate change. In 2009,
transport was responsible for 23% of global GHG emissions compared with 41% for
energy. By 2035, it is expected to become the single largest GHG emitter
accounting for as much as 46% of global emissions, and it is set to reach 80%
by 2050 [1].
Evidently,
climate change is real, and human activities, particularly transport-related
emissions, are a major dominant cause [13,23,29,37,47,49]. Today, changes in
the climate are observed in all geographical regions of the globe: the
atmosphere and oceans are warming, the extent and volume of snow and ice are
diminishing, sea levels are rising, and weather patterns are changing.
Anthropologic GHG emissions from transport are a key contributor to global
climate change, with carbon dioxide representing the largest proportion of the
emissions. Over the past three decades, carbon dioxide emissions from transport
have risen faster than those from all other sectors and are projected to rise
more rapidly. Presently, industrialised countries are the main sources of
transport emissions. However, the proportion of emissions being produced in
developing countries is rapidly increasing. The majority of transport fuel
emissions (76%) are from road transport, including four-wheeled vehicles and
personal pickup trucks. Air travel produces around 12% of transport carbon
dioxide emissions, and its share is fast growing as well [13].
There are
indications that changes in climatic conditions will continue under a range of
possible GHG emission scenarios over the 21st century. If the current trends in
emissions continue, their impacts by the end of this century are projected to
include a global average temperature that is between 2.6 and 4.8°C higher
than what it is presently, and sea levels 45-82 cm higher than present as
well. Even if emissions are stopped today, temperatures would remain elevated
for centuries owing to the effect of the accumulated greenhouse gases from past
human emissions present in the atmosphere. Thus, limiting temperature rise
would require substantial and sustained reductions of GHG emissions, including
those emanating from the transport sector.
Interestingly,
the transport sector is both the culprit and the victim of climate change. This
is because the far-reaching impacts of climate change are diverse; intense
droughts and floods, heat waves, thawing permafrost and sea-level rise, which
could damage such transport infrastructure as roads, railways, airports and
seaports, requiring extensive adaptation and changes to route planning in some
cases. Road assets are particularly vulnerable to climate stressors such as
higher temperatures, increased precipitation or flooding [11]. Virtually, all
models show that weather extremes will indeed put considerable pressure on the
road system, particularly in Africa. The damage and accelerated ageing of roads
caused by climate change will require increased maintenance and frequent
rehabilitation. Apart from these, climate-related damage to the road
infrastructure will cause more frequent disruptions to the movement of people
and goods, with direct consequences on economic productivity.
Furthermore,
climate change has serious significant adverse effects on not only road
transport but also on other major transport systems and modes as well [23]. For
instance, rail beds are especially susceptible to the aftermaths of climate
change including increased rainfall, flooding and subsidence, sea-level rise,
and increased incidence of freeze-thaw cycles. More so, thawing permafrost may
lead to ground settlement, which then undermines the stability of railways. Additionally,
higher temperatures pose a threat to rails through thermal expansion and
buckling. Underground electric rail systems are similarly vulnerable to heat
waves and flooding. Even air transport is not immune to the consequences of
climate change impacts on the transport sector as more storms in some regions
of the world may increase the number of weather-related delays and
cancellations. Clear-air turbulence is likely to increase in the Atlantic
corridor, leading to longer and bumpier trips. Further, more intense heat and
rainfall will have similar impacts on airport runways as on roads. Eventually,
higher temperatures at high-altitude and low-latitude airports may reduce the
maximum takeoff weight or require investment in longer runways owing to less dense
air.
Water
transport and coastal infrastructure are vulnerable to the impacts of climate
change on transport as well. More frequent droughts and floods may force
businesses to use smaller vessels for inland shipping, which will raise
shipping costs [23]. Some inland waterways are projected to be useable for
fewer days each year because of more intermittent water availability. On the
ocean, a projected increase in storms in some regions could raise the cost of
shipping by forcing ships to take longer routes that are less storm-prone.
Subsequently, more frequent delays and cancellations of ferries could result
from extreme weather events. Even with the projection of the Arctic Ocean
becoming progressively more accessible to shipping in summer as sea-ice extent
decreases, with a virtually ice-free ocean likely by mid-century, the increase
in shipping through sensitive ecosystems could lead to an increase in serious
local environmental and climate change impacts.
In time,
roads, rail and airports near the coast will become more vulnerable to flooding
and erosion due to sea-level rise and extreme weather events, as will ports.
Extreme events projected to increase include intense rainfall, high winds and
storm surges. Globally, the value of all coastal assets exposed to flooding was
estimated at 5% of gross domestic product (GDP) in 2005. This has been
projected to rise to as high as 9% in 2070 [23]. All these point to the cause
and effect relationship between transport and climate. It is such that
activities in the transport sector invariably have far-reaching implications
for the climate, and changes in climate impact significantly on the transport
sector.
2. THE SOUTH
AFRICAN TRANSPORT SECTOR AND CLIMATE CHANGE
Transport
systems form the backbone of South Africa's socioeconomic activities, enabling
the movement of people and products. Therefore, transport and the demand for it
has become an integral part of the daily lives of South Africans. The movement
of goods and services in time and space defines and influences, and is impacted
upon by economic activities. Demands for transport shape the urban landscape
and influence the spatial choices that the citizenry makes concerning social
and economic services such as place of residence, education and work. Business,
in similar ways, makes locational choices based on market proximity and size,
as well as considerations for ease of temporal and spatial mobility of labour,
goods and services. These choices contribute in a major way to the wellbeing of
individuals, households and businesses in the country [21]. Meanwhile, the
transport sector in South Africa is confronted with the legacy of apartheid
spatial planning, which has resulted in displaced urban development and
distorted, fragmented, unequal and inefficient human settlement patterns that
result in the movement of people across long distances from home to work. Thus,
transport networks are poorly integrated with the majority of the citizens
living far from their workplaces. Consequently, many have to commute over long
distances. These travel patterns have a substantial impact on air quality,
climate change and ozone layer depletion [15,20,21,43].
Research has shown that a steady
increase in household incomes directly translates into increased consumption
and demand for transport. Accordingly, as South Africans earn more, they tend
to end up buying more cars. However, there are externalities associated with
this tendency, particularly in environmental terms. Emissions from the
transport sector in South Africa account for 13% of the country’s total
GHG emissions, of which 86% is from the combustion of liquid fossil fuels. In
addition to these direct emissions arising from the combustion of fuels,
indirect emissions arise from the production, refining and transport of
transport fuels. South Africans pay dearly for their auto-dependency
predilections largely in form of traffic congestion, especially during peak
hours. This brings about an increase in trip times and restrictions in
mobility, which has far-reaching psychological, economic and environmental
ramifications. Generally, overall productivity is adversely affected [21,25].
Transport is the primary consumer
of liquid fuels in South Africa [39]. Demand for energy in this sector is
forecast to grow to 24–37% of total energy demand by 2050, possibly
representing the largest sectoral demand for energy in South Africa [18,21].
The South African transport sector is estimated to emit 60 Mt CO2eq
and require 800 PJ of energy, similar in scale to the industrial energy demand
and emissions [2]. The sector is forecast to potentially eclipse the industry
in this regard if conventional vehicle choices and travel modes persist.
Greenhouse Inventory for South Africa, covering the period 2000 to 2010,
revealed that GHG emissions from transport increased by 32% from 36,016 Gg CO2eq
in 2000 to 47,607 Gg CO2eq in 2010. Road transport was responsible
for 91.2% of GHG emissions from the sector during this period. If these trends
continue in the absence of mitigating legislation and policies, the transport
sector is projected to emit a total of 136 Gg CO₂eq
by the year 2050 [16,43,62]. In addition, it has been stated that South Africa
ranks 13th globally on carbon dioxide emissions contributions, and is one of
the top 10 carbon-intensive major economies in the world (GDP larger than $200
billion), with a carbon intensity of 0.972 metric tons of CO2 per
$1000 of GDP in 2011 [27]. This competitively compares to leading countries
such as Germany at 0.290 t CO2 per $1000 of GDP, or China at 0.804 t
CO2 per $1000 of GDP [51,54,60].
Noticeably, one underlying factor
for the foregoing GHG emission records in South Africa is the high rate of
production and sales of motor vehicles in South Africa. Domestic production of
motor vehicles in the country surged from 601,178 vehicles produced in 2017 to
about 610,000 vehicles in 2018 [59]. Meanwhile, an improvement in industry
vehicle production of about 8.0% was projected for 2019 to reach about 657,500
units. Table 1 gives a five-year outlook for vehicle sales in South Africa.
It is on record that
South Africa has the highest cars per capita in Africa as one in every five
people in the country owns a vehicle [5]. In 2012 alone, more than 250,000
units were sold in South Africa alone. At the end of February 2017, there were
12,027,860 registered vehicles in South Africa [55]. This makes South Africa
one of the largest vehicle markets in Africa and a high emitter in per capita
terms with 10.3 t CO2 per person (t cap-1), which is above the
global (6.3 t cap-1) and sub-Saharan Africa (3.2 t cap-1) averages [3]. Given
this scenario, the scientific consensus is that sub-Saharan Africa, with
its geographic location straddling the equator, will experience the greatest
negative effects of global warming of all the regions. For South Africa, under
the current emissions trajectory, there is projected to be an average increase
above the 20th century average of 1.5°C around the coast to 3°C in the
interior by 2050, with a doubling of these figures to 3 and 6°C by the end
of the century. These changes come with dire consequences [58].
Tab.
1
A
Five-Year Sales Outlook for Domestic Vehicle Sales in South Africa (2015-2019)
Sector |
2015 |
2016 |
2017 |
2018 |
2019 Estimates |
Cars |
412,478 |
361,264 |
368,114 |
365,246 |
368,000 |
Light Commercials |
174,701 |
159,283 |
163,317 |
159,452 |
162,000 |
Medium Commercials |
10,394 |
8,315 |
7,890 |
7,913 |
8,000 |
Heavy/Extra Heavy/ Commercials/Buses |
20,075 |
18,685 |
18,382 |
19,579 |
20,000 |
Total Vehicles |
617,648 |
547,547 |
557,703 |
552,190 |
558,000 |
Source: Wheels24 [59]
3. TRANSPORT DECARBONISATION STRATEGIES IN
SOUTH AFRICA: AN OVERVIEW
Many countries and
non-state actors have expressed the need for a global leadership platform in
support of aggressive actions on transport and climate change. In 2017, for instance,
the establishment of a Transport Decarbonization Alliance (TDA), composed
of countries, and other entities committed to ambitious action on transport and
climate change, was proposed [47]. The alliance brings together more than 150
organisations, networks and initiatives that support ambitious, transformative
action on transport and climate change. Along this line, South Africa has some
decisive steps towards cutting down carbon emissions. The country has a
well-developed base to effect climate change mitigation and adaptation [42].
The country has initiated Climate Change Flagship Programmes to respond to the
three key challenges facing it even as global efforts to address climate change
intensify. These programmes encompass demonstrating the course of actions
needed to respond to climate change, attracting resources at the scale required
to enable meaningful transformation, and igniting national-scale action at the
speed required to respond to climate change. In addition, Low Carbon, Climate
Resilient Transport Systems is duly recognised as one of the major components
of the Climate Change Flagship Programmes Goals to 2030.
Specifically, South
Africa has committed to reducing its GHG emissions by 34% by 2020 and 42% by
2025, relative to a ‘business-as-usual’ baseline. This is in the
realisation of the country’s ranking as one of the world’s largest
GHG emitting country in absolute terms in 2007, with per capita emissions
nearly twice the global average [4,51,60]. According to the Sustainable Development
Solutions Network (SDSN) and the Institute for Sustainable Development and
International Relations (IDDRI) [53], South Africa is committed to contributing
its fair share to global GHG mitigation efforts to keep the temperature
increase well below 2°C. With financial, technology, and capacity-building
support, this level of effort will enable South Africa’s GHG emissions to
peak between 2020 and 2025 in a range with a lower limit of 398 Mt CO2eq
and upper limits of 583 Mt CO2eq and 614 Mt CO2eq for
2020 and 2025, respectively. Plateau with a lower limit of 398 Mt CO2eq
and upper limit of 614 Mt CO2eq for approximately a decade, and
decline in absolute terms thereafter to a range with a lower limit of 212 Mt CO2eq
and upper limit of 428 Mt CO2eq. This is referred to as the Peak
Plateau Decline (PPD) benchmark trajectory.
To achieve these
goals, South Africa is committed to decarbonisation efforts by taking conscious
steps towards achieving a low-carbon economy through a reduction in carbon
emissions. So far, the country has taken steps to:
1. continue to put in place transport policies and
developments that result in a modal shift in passenger transport to public and
low carbon forms of transport including plans to move freight from road to rail
over time,
2. encourage the integration of land use and
transportation planning in cities in a manner that encourages public transport,
non-motorised transport (walking and cycling) and promotes alternative
communication methods such as telecommuting to reduce long term transport fuel
use patterns,
3. improve the efficiency of the country’s vehicle
fleet across board through a range of measures including the use of fuel
standards,
4. invest in the further development and deployment of
cleaner technologies for the transport sector such as electric vehicles and
hybrids,
5. build capacity to deal with transport mitigation in
the areas of planning, engineering, and relevant technical skills,
6. support the production and use of cleaner fuel
technologies and alternative fuels away from current fossil fuels,
7. implement the flat rate specific excise tax based on
passenger vehicle carbon emissions, which applies to each gram of carbon
dioxide vehicle emissions above a target range, and investigate expanding the
emissions tax to include other categories of motor vehicles,
8. consider further incentives in the form of lower fuel
taxes to encourage cleaner fuels and integrate climate change information into
transport planning to minimise the potential risk to infrastructure from
extreme weather events [43].
In addition, to
address the environmental and infrastructure implications of unmitigated growth
in conventional fuel consumption and travel modes, the Department of Transport
published the draft Green Transport Strategy (GTS) [21]. The GTS is guided by
the National Climate Change Response White Paper and National Development Plan,
which outlines South Africa’s commitment to climate change interventions
in line with the 2015 United Nations Climate Change Conference (COP 21) and
affordable transport systems [14]. The GTS aims to reduce harmful emissions and
negative environmental impacts associated with transport systems and has become
the primary reference for policy interventions. The interventions identified
for implementation in the South African multi-sector energy-economic modelling
framework, otherwise known as the South African TIMES Model (SATIM) are:
i.
30% shift in freight transport from road to
rail by 2022,
ii.
20% shift in passenger transport from private
cars to public transport and non-motorised transport by 2022,
iii.
20% of the public sector fleet and 10% of the
national fleet comprising electric or hybrid vehicles by 2022,
iv.
All (metro) public and quasi-public (minibus)
transport vehicles to move to a natural gas and petrol dual-fuel system within
10 years,
v.
10% of the urban bus fleet to be converted to
gas-only vehicles per year,
vi.
10% of the Metrobus fleets to be converted to
gas-only vehicles per year,
vii.
Fuel levy relief (50% exemption for biodiesel
and 100% exemption for bioethanol),
viii.
Fiscal policies such as the imposition of a carbon tax.
Moreover, with
additional growth expected in road transport demand, emissions are similarly
expected to further increase over the next decades [40,41]. Therefore, South
Africa faces the need to modernise and expand its transport infrastructure
while simultaneously significantly reducing transport-related emissions [9].
Recently, the country implemented several climate strategies and policies in
the transport sector, which have been implemented to a variable degree. Table 2
gives an overview of these currently implemented and planned sectoral climate
policies.
Tab.
2
Climate
Change Policies for the Transport Sector in South Africa
Changing
Activity |
Energy Efficiency |
Renewables |
Nuclear/CCS/Fuel Switch |
Urban
planning and infrastructure
investment to minimise transport needs: ▪ Draft Green
Transport Strategy (GTS) 2017– 2050 (2017) ▪ National Rail Policy Green Paper (2015) ▪ National Transport Master Plan (2010) ▪ Public Transport Strategy (2007) |
Minimum
energy/ emissions
performance standards or support for
energy efficient for
light duty vehicles: ▪ Vehicle labeling scheme (2008) ▪ Vehicle fuel economy norms and standards
(since 2005) |
Biofuel
target: ▪ Regulations Regarding the Mandatory Blending of Bio-fuels with Petrol and Diesel (2012) ▪ Biofuels Industrial Strategy (2007) |
Support
for share switch: ▪ Draft Green
Transport Strategy 2017–2050 (2017) ▪ National Transport Master Plan (2010) ▪ Bus Rapid Transit Systems (BRT) on city- level (since 2010) |
|
Minimum
energy/ Emissions
performance standards or support for energy efficiency for heavy-duty vehicles:
None |
Support
schemes for biofuels: ▪ Regulations on Mandatory Blending of Bio-fuels with Petrol and Diesel (2012) ▪ Biofuels Industrial Strategy (2007) |
E-mobility
programme: ▪ Electric Vehicle Industry Roadmap (2013) |
|
|
Sustainability
standards for biomass
use: None |
|
Tax on fuel and/or emissions: ▪ Carbon
Emissions Motor Vehicles Tax (2010) ▪ General
Fuel Levy (1983) |
|||
Fossil fuel subsidies: None |
Source: CAT [9]
The information
provided in Table 2 consists of existing, planned and potential climate change
policies for the transport sector in South Africa. However, it should be noted,
as indicated in the table, that no policies currently exist on minimum
energy/emissions performance standards or support for energy efficiency for
heavy-duty vehicles, sustainability standards for biomass use, and fossil fuel
subsidies in South Africa. Subsequently, the country would adopt appropriate
policies from other countries where such exist. The blank cells indicate that
no policies currently exist and a similar policy gap exists in all other
countries as well. In addition, the Ministry of Transportation released a Draft
Green Transport Strategy (GTS) 2017-2050 in August 2017. Although the
prioritised policy interventions aim to address the country’s transport
needs and directly combat emissions in the transport sector, efficient
implementation of the proposed measures and sufficient funding remain critical challenges
[21].
Another major
initiative towards the decarbonisation of the transport sector in South Africa
is a switch in modal share of passenger transport through the launch of the Bus
Rapid Transit Systems (BRT) in eight cities and municipalities, to start with.
Other model switch policy initiatives mentioned in the Draft GTS 2017-2050 aim
to upgrade the mini-bus taxi industry, intelligent urban transport systems
integrating public transport and the minibus industry, and non-motorised
transport infrastructure [21]. However, no modal shift policies have been
implemented for freight transport as of December 2017. The policy objective
behind the National Rail Policy Green Paper of 2015 is to proactively
facilitate shifting freight and passengers from road to rail and to promote
rail as the mode of choice by providing an efficient, reliable and safe setting
for passengers and freight [19]. However, no concrete policy action is
currently in place [9].
In addition, vehicle
fuel-economy norms and standards for newly manufactured vehicles from 2005
onwards were introduced in South Africa [50,57]. In the Draft GTS 2017-2050,
the Ministry of Transport states its intention to revise the level of
vehicle fuel economy emission standards with unclear implications for
transport-related carbon dioxide emissions [21]. However, a gradual tightening
of general emission standards will not be sufficient to be in line with the
required 1.5°C trajectory even if South Africa introduces higher carbon
emissions motor vehicle tax levels [9,10]. Other national policies and
regulatory frameworks that form the legislative foundation for the development
of the Green Transport Strategy in South Africa include the Constitution of the
Republic of South Africa; the White Paper on National Transport, 1996; White
Paper on Energy Policy, 1998; National Environmental Management Act 107 of 1998
(NEMA); the National Freight Logistics Strategy, 2005; Public Transport
Strategy, 2007; National Land Transport Act, 2009; White Paper on National Climate
Change Response Policy, 2011; the Spatial Planning and Land Use Management Act
16 of 2013 (SPLUMA); National Transport Master Plan (NATMAP), 2016, and several
other regulations on petroleum products and pipeline.
The abovementioned
notwithstanding, in the light of current attains, South African transport
sector is not likely to meet the two actionable benchmarks. More so, already
implemented policies such as the mandated biofuel blending and fuel-economy
norms and standards are projected to have very limited impact on the overall
emission levels of the South African vehicle fleet. This is due to a lack of
incentives for the promotion of zero-emission vehicles and required
infrastructure as South Africa currently makes no progress to phase out fossil
fuel car sales between 2035 and 2050 to significantly increase the share of
non-emission vehicles. Besides, it has been observed that the majority of
existing environmentally-related taxes were introduced with the primary
intention of raising revenue [21]. Thus, it is arguable that environmental
outcomes are only by products of the imposition of carbon taxes in the country.
Even in the field of aviation and shipping where South Africa has initiated
some minor activities to reduce emissions, efforts have not been made to
develop 1.5°C compatible vision. Table 3 summarises the progress made so
far on the most important steps to decarbonise the transport sector in the
country.
Tab. 3
South Africa’s Transport Sector Progress on Limiting Temperature
Increase
1.5 °C-Consistent Benchmark |
Projection(s)
under Current Policies |
Gap Assessment
(Qualitative) |
Last fossil fuel car sold before 2035 |
Low projected growth in electric vehicle uptake, similar at best to projections for Rest of World in BNEF 2017 with around 1% EV share in new car sales by 2020 and share of 40–50% by 2040 |
+ Overarching Green Transport Strategy (GTS) until 2050
defining policy priorities for each area of transport in South Africa + Several policies in place in the transport sector aim
to reduce emissions from passenger vehicles, however, have relatively low
level of expected impact - No overarching 1.5°C compatible vision for the
transport sector in South Africa - Uncertainty about enforcement of biofuel quota
programme due to sustainability concerns, but only marginal impact if fully
implemented - Insignificant share of electric vehicles sales and no
policies in place to promote and incentivise the use of EVs - Freight transport-related emissions expected to
increase substantially under current policies with the growing use of road
networks for freight transportation |
Aviation and shipping: Develop and agree on a 1.5°C compatible vision |
• Expected increase of international aviation emissions by 75% until 2030 and
289% until 2050 compared to 2016 under currently implemented policies in South Africa • No projections available for maritime shipping in South Africa |
+ Department of Transport actively engages in
ICAO’s initiatives to reduce emissions, while currently prioritising
improved Air Traffic Management (ATM) and infrastructure use for South Africa - No intention announced to participate in ICAO’s
CORSIA carbon offsetting and reduction scheme - Relatively small emission reductions of currently
implemented measures in the aviation sector, whereas other measures for use
of alternative fuels and airport improvements are only in early planning
stages - There are no strategy or policies on greener or
sustainable maritime shipping in South Africa - Inadequate policy initiative to improve rail freight
transport to enable a modal shift in the freight transport sector |
Source:
Adapted from CAT [9]
It is important to
note that the two major short-term actionable benchmarks featured in Table 3
are just getting started; as such, it is too early to embark on any objective
evaluation. These are: that the last fossil car needs to be sold before 2035 to
achieve car fleets consisting of 100% zero-emission cars by 2050 and that a
1.5°C compatible vision for the aviation and shipping needs to be developed
and agreed upon. With the findings of the Intergovernmental Panel on Climate
Change (IPCC) on achieving net-zero carbon dioxide emissions around 2050 and
the rapid update electric vehicles of the last years in mind, this
analysis decides to strengthen the benchmark for the vehicle sales to a full
100% zero-emissions car stock by 2050, meaning the last fossil car needs to be
sold before 2035 [35].
Research constitutes
another important dimension to efforts towards the decarbonisation of the South
African transport sector. Thus, several studies with implications for the
sector have been conducted. Generally, most of these studies were conducted on
the overall energy sector; however, the implications for the transport sector
are evident in their findings. For example, Altieri et al. [3] examined the
implications of meeting a cumulative carbon constraint between 2015 and 2050 of
14 Gt of carbon dioxide equivalent (CO2eq), in scenarios considering
different economic development pathways for South Africa. According to the
study, the emissions constraint was met by a rapid decarbonisation of
electricity supply and a move away from emissions-intensive gas-to-liquids and
coal-to-liquids. Further, the study found that the rapid and relatively lower
cost decarbonisation of the electricity system encourages demand sectors to
increase their dependence on electricity. Evidently, this has implications for
the transport sector where an opportunity emerges for a large-scale switch to
electro-mobility technologies, including battery electric, hydrogen fuel cell,
and hybrid vehicles. Such a transition would address one of the main concerns
about plug-in vehicles because the carbon emissions simply move from the
vehicle’s exhaust to the power station [30].
In a follow-up study,
Caetano et al. [7] analysed an even more rapid transition to decarbonised
energy in South Africa assuming a more stringent constraint of 10 Gt cumulative
emissions from 2015 to 2050. To meet this carbon constraint, the electricity
sector would undergo a rapid transition leading to higher electricity prices
between 2020 and 2040. The electricity price increases owing to the increase in
the electricity sector investment requirements, which has a slightly negative
impact on the economy. The cumulative impact of the transition is estimated at
just over 4% of total GDP in 2040. However, as the cost of renewable energy
continues to decline rapidly beyond expectation, these negative impacts of the
transition are likely to fall away. Apparently, the focus of these studies was
mainly on the rapid transition in the electricity sector as a response
mechanism. The potential opportunities that a decarbonised electricity sector
could provide for the transport sector have not been explored. Meanwhile, the
significance of transport in total final energy demand in South Africa, the
country’s high reliance on crude oil imports, and increasing global
electro-mobility make these opportunities attractive to explore [7]. In
addition, an attitudinal problem has been identified towards decarbonisation in
South Africa. Specifically, attitudes towards using only energy-efficient
vehicles when outsourcing or using own vehicles, the importance of
sustainability for the country, and the importance of carbon dioxide emissions
for the country are not encouraging [27].
From the foregoing,
it is obvious that enough serious attention has not been paid to active
transport in the decarbonised transport policy formulation. Although usually,
it is casually mentioned with mere lip service paid to it in one policy
statement or the other, however, no concrete practical step has been
conscientiously taken so far to accord it the pride of place it deserves in the
discourses and action plans in the transport sector of the country. As it is,
none of the empirical studies has prioritised it, as all forms of active
transport have been largely neglected with only public transport mentioned en
passant. Meanwhile, the inclusion of active transport in the overarching
decarbonised transport policy formulation anywhere cannot afford to limit the
inclusion of active transport to mere conceptual-cum-theoretical colouration.
Practical steps to prioritise it are indispensable.
4. TRANSPORT
DECARBONISATION IN SOUTH AFRICA: THE ROLE OF ACTIVE TRANSPORT
If South Africa would
ever achieve her goals and targets of transport decarbonisation, the indispensability
of active transport cannot be overemphasised, especially when all the steps
taken so far do not seem to promise the much desired effect. Active transport
is well captured in the Africa Development Bank’s (ADB’s) blueprint
for mitigating climate change in transport [1]. ADB proposes the Avoid-Shift-Improve
Approach, a promising conceptual tool to chart the course of mitigating climate
change in transport at country and regional levels. According to the Bank,
Avoid means reducing the need to travel, for example, by integrating land use
and transport planning to create local clusters of economic activities that
require less mobility; by changing how production is organised (for example,
doing more online); and by developing multimodal logistic chains to cut
wasteful and unnecessary trips. Shift means changing to more
energy-efficient modes or routes such as shifting from road to rail or
waterways or onto well-defined trucking routes; or shifting passengers from
private vehicles to public transport and non-motorised modes. Improve entails
using technologies that are more energy efficient including through improving
vehicle standards, inspection and enforcement; developing improved vehicle
technologies and fuels; and improving transport efficiency using information
technology. Evidently, both Avoid and Shift favour active transport. By
integrating land use and transport planning to create local clusters of
economic activities that require less mobility, active transport would be
promoted and carbon dioxide emission significantly reduced. The outcome
would be phenomenal when the use of rail and other public transport as well as
non-motorised modes is popularised as well.
Active transport
includes non-motorised forms of transport involving physical activity, such as
walking and cycling, as well as public transport to meet longer distance trip
needs as public transport trips generally include walking or cycling components
as part of the whole journey [44,56]. There has been a continued increased
academic interest in the active transport research, mainly from the perspective
of health benefits, safety and ways in which urban design can promote more
sustainable travel [22,31,48]. However, these studies mostly emphasise the
importance of making active transport an easy choice through good urban design,
restrictions on car use and land-use planning that enables services to be
accessed without motorised transport [45]. Only a few studies directly relate
the promotion of active transport to carbon reduction and climate change [12,28,36].
Walking and cycling
constitute the ultimate zero carbon and environment-friendly solution for
personal transport. However, both walking and cycling have significantly
declined for years, becoming unpopular [12,17,44]. Empirical evidence shows
that the decline in walking and cycling is a reflection of the growth and
affordability of the motor car and a series of psychological and sociological
factors [6,21,44] that range from a generally poor level of fitness as well as
safety and security issues to unfavourable weather and physical factors [12,44].
Nevertheless, the South African Department of Transport [21] identified the
modal shifts from private car usage to public transport (particularly rail) and
non-motorised transport as being essential actions needed to reduce energy
consumption and GHG emissions. This necessarily implies that South Africa is
very unlikely to achieve the much desired carbon decarbonisation without
recourse to active transport.
Research undertaken
by research organisations on behalf of the South African government indicates,
among other things, the imperativeness of implementing measures that will
reduce the need to travel and avoid unnecessary trips through walkable
communities, integrated land use planning, transit-oriented development, and
improving vehicle occupancy rates [21]. Furthermore, it was found that given
that the road transport sub-sector is responsible for 91.2% of direct emissions
from transport, shifting of passengers to public transport and freight to rail
is a necessity. Besides, several sustainable transport instruments that double
as decarbonised transport instruments have also been identified [13]. These
instruments clearly emphasise land use planning that prioritises non-motorised
modes (walking and cycling) as well as planning for public transport modes,
including buses, rail, light rail, metro and underground systems.
It must be
acknowledged that as desirable and important as active transport is in
achieving the goals of transport decarbonisation, sight should not be lost of
the right attitude and behaviour towards it. This is because research has found
that people, especially in Africa, generally tend towards auto-dependency for
as long as they can afford it [44]. Behavioural change programmes are essential
as reducing traffic from short journeys will not only reduce the environmental
impacts but also make society healthier as a whole. To make walking and cycling
a real alternative for local trips, every local authority, business and school
needs to consider ‘soft’ transport policy measures to promote them
[8,24,32,33,34,52]. Towards this end, many relatively simple improvements can
be made. Reallocation of space is crucial to increase the safety of zero carbon
journeys. This would take the form of cycle lanes and pedestrian areas linked
with improved road crossings and safer junctions which are required for a
sustainable street for all modes [38]. However, local measures are not complete
solutions to make walking and cycling more viable. The main factor behind a
decline in zero-carbon trips is that fewer destinations are within walking and
cycling distance [12,46].
Underscoring the
importance of policy intervention towards engendering active transport,
Farrag-Thibault [23] argued that the transition required to dramatically reduce
GHG emissions needs system-wide strategies that combine, among other things,
modal change, stringent sustainable transport strategies, and profound
behaviour change. This was similarly corroborated by Chapman [12], who posited
that to achieve a stabilisation of GHG emissions from transport, a behavioural
change brought about by policy will be required. Therefore, the key aims to
achieve reduced GHG emissions from transport should not be limited to
alternative fuels, energy sources or technology as typically emphasised in
South Africa, but should also include a change in travel behaviour and modes.
Usually, technology improvements are most effective when implemented in
conjunction with other instruments within a larger strategy.
Policy interventions
towards engendering active transport cannot possibly be effective in the
absence of certain regulatory instruments. The following regulatory
instruments, largely informed by Dalkmann and Brannigan [13], would go a long
way in creating a culture of active transport in South Africa.
5. CONCLUSIONS AND
RECOMMENDATIONS
The ambitious
decarbonisation goals of South Africa’s transport sector are attainable.
However, if they must be achieved, decision makers have to look beyond the
previously seemingly closed list of approaches that do not accord active
transport the pride of place it deserves, and acknowledge its proven efficacy.
Admittedly, barriers to the overarching integration of active transport are
real. They include high facility investment (especially in terms of new cycling
lanes and dedicated BRT lanes), and the expense associated with transforming or
decommissioning existing infrastructure as well as ingrained social norms and
attitudinal idiosyncrasies that characterise Africans where vehicle ownership
often symbolically defines socioeconomic status. More so, while alternatives
are becoming available, significant policy intervention will be critical to
generalising low-carbon technologies and practices for mass transit modes.
Conscious steps that
prioritise the aggressive pursuance of measures, which conscientiously target
active transport should be adopted and followed through. Also, norms and
standards for transport decarbonisation should be developed at the national,
provincial and local levels to ensure that there is consistency in the active
transport policies that are implemented across different jurisdictions. These
should be towards achieving a modal shift in passenger travel in the country.
As much as possible, the use of private cars should be discouraged while active
travellers should be given all the required support and motivation. Afterwards,
the South African rail system should be thoroughly explored to avail the
country all the opportunities it has to offer as a veritable mass transit mode
of choice. Meanwhile, some facility and infrastructural investments and
retrofitting should be made. For instance, BRT systems need to be significantly
expanded with their security, reliability and frequency enhanced.
In addition,
non-motorised transport infrastructure, specifically the building of cycle
lanes along key transport routes as well as improved pavements and sidewalks,
measures aimed at enhanced walkability must be included in the maintenance
mandates of all relevant agencies. This is imperative if public desire and
support for non-motorised transport are to be obtained. Most importantly, South
Africans should be educated on the need to embrace active transport irrespective
of social class. The great health benefits of active transport can be
accentuated to drive home the point that auto-dependency related diseases are
no respecters of persons or status. Moreover, all avoidable auto-dependent
trips should be eliminated. Finally, public transport should be made more
efficient and their drivers more time-conscious and businesslike.
References
1.
ADB. 2019. “Addressing Climate Change
in Transport”. Available at: https://www.adb.org/sectors/transport/key-priorities/climate-change
2.
Ahjum F., B. Merven, A. Stone, T. Caetano.
2018. “Road Transport Vehicles in South Africa towards 2050: Factors
Influencing Technology Choice and Implications for Fuel Supply”. Journal of Energy in Southern Africa 29(3):
33-50. DOI: http://dx.doi.org/10.17159/2413-3051/2018/v29i3a5596.
3.
Altieri K.E., H. Trollip, T. Caetano, A.
Hughes, B. Merven, H. Winkler. 2016. “Achieving development and
mitigation objectives through a decarbonization development pathway in South
Africa”. Climate Policy 16(1):
S78-S91. DOI: 10.1080/14693062.2016.1150250.
4.
Alton T., C. Arndt, R. Davies, F. Hartley, K.
Makrelov, J. Thurlow, D. Ubogu. 2013. “Introducing carbon taxes in South
Africa”. Applied Energy 116:
344-354.
5.
Be Forward. 2018. “Which African
Countries Have the Most Cars on the Road?” Available at: https://blog.beforward.jp/regional-topics/africa/cars-capita-africa-country-cars-road.html.
6.
Black C., A. Collins, M. Snell. 2001.
“Encouraging Walking: The case of journey-to-school trips in compact
urban areas”. Urban Studies 38:
1121-1141.
7.
Caetano T., B. Merven, F. Hartley, F. Ahjum.
2017. Decarbonisation and the Transport Sector: A Socio-Economic Analysis of
Transport Sector Futures in South Africa.
Journal of Energy in Southern Africa 28(4): 9-18.
DOI: http://dx.doi.org/10.17159/2413-3051/2017/v28i4a2945.
8.
Cairns S., L. Sloman, C. Newson, J. Anable,
A. Kirkbride, P. Goodwin. 2004. Smarter
Choices – Changing the Way We Travel. UK Department of Transport.
9.
CAT 2018. Scaling
Up Climate Action: Key Opportunities for Transitioning to a Zero Emissions
Society. Full Report, CAT Scaling Up Climate Action Series, South Africa,
November.
10.
CAT. 2016. The Ten Most Important Short-Term
Steps to Limit Warming to 1.5°C. Climate Action Tracker (Climate Analytics,
Ecofys, New Climate Institute). Available at: http://climateactiontracker.org/assets/publications/publications/CAT_10_Steps_for_1o5.pdf.
11.
Cervigni R., A.M. Losos, J.L. Neumann, P.
Chinowsky. 2017. Enhancing the Climate Resilience of Africa’s
Infrastructure: The Roads and Bridges Sector. Washington, DC: World Bank
Group. Available at: http://documents.worldbank.org/curated/en/270671478809724744/Enhancing-the-climate-resilience-of-Africa-s-Infrastructure-the-roads-and-bridges-sector.
12.
Chapman L. 2007. Transport and Climate
Change: A Review. Journal of Transport
Geography 15: 354-367.
13.
Dalkmann H., C. Brannigan. 2010. Sustainable Transport: A Sourcebook for
Policy-makers in Developing Cities. Eschborn: Deutsche Gesellschaft
für Internationale Zusammenarbeit (GIZ) GmbH. Available at: https://www.sutp.org/files/contents/documents/resources/A_Sourcebook/SB5_Environment%20and%20Health/GIZ_SUTP_SB5e_Transport-and-Climate-Change_EN.pdf.
14.
DEA. 2011. “National Strategy for
Sustainable Development and Action Plan”. Available at: https://www.environment.gov.za/sites/default/files/docs/sustainabledevelopment_actionplan_strategy.pdf.
15.
DEA. 2013. GHG inventory for South Africa
2000-2010. Pretoria: DEA.
16. DEA. 2014. South Africa’s Greenhouse Gas
Mitigation Potential Analysis - Annex G: AFOLU Sector. Pretoria: DEA.
17.
DfT. 2004. Walking and Cycling: An Action Plan. UK Department for Transport,
Crown Copyright.
18.
DoE. 2016. Draft Post-2015 National Energy
Efficiency Strategy. Pretoria:
DoE. Available at: https://www.gov.za/sites/www.gov.za/files/40515_gen948.pdf.
19.
DoT. 2015. National Rail Policy: Green
Paper. Pretoria: DoT. Available at: http://www.transport.gov.za/LinkClick.aspx?fileticket=0MTIGeNPZ8s%3D&tabid=334&mid=1800.
20.
DoT. 2016. National Transport Master Plan
(NATMAP) 2050. Pretoria: DoT.
21.
DoT. 2017. Draft Green Transport Strategy 2017-2050 - Draft. Available
at: https://roadtransportnews.co.za/wpcontent/uploads/2017/08/Draft-Green-Transport-Strategy.pdf.
22.
Elvik R. 2009. “The non-linearity of
risk and the promotion of environmentally sustainable transport”. Accident Analysis and Prevention 41:
849-855.
23.
Farrag-Thibault A. 2014. Climate Change: Implications for Transport. The Fifth Assessment
Report from the Intergovernmental Panel on Climate Change. Cambridge:
University of Cambridge.
24.
Gündling Felix, Florian Hopp, Karsten
Weihe. 2020. „Efficient monitoring of public transport journeys”. Public Transport 12: 631-645.
25.
Harriet T., K. Poku, E.K. Anin. 2013.
“Logistics Inefficiencies of Urban Transportation System in Ghana”.
International Journal of Humanities and
Social Science 3(6):
308-314.
26.
Havenga J., L. Goedhals-Gerber, H. Freiboth,
Z. Simpson, A. De Bod. 2015. The Decarbonisation
of Transport Logistics: A South African Case. Canadian Transportation
Research Forum. Available at: https://trid.trb.org/view/1417744.
27. Havenga J., L-A. Terblanche, L. Goedhals-Gerber, Z.
Simpson. 2018. “South
Africa’s Road Freight Decarbonisation Experiences”. A presentation
at the Decarbonising Road Freight Workshop of ITF-OECD. 28-29 June. Paris.
28.
Higgins P., M. Higgins. 2005. „A
healthy Reduction in Oil Consumption and Carbon Emissions”. Energy Policy 33: 1-4.
29.
IEA. 2005. CO2 Emissions from Fuel Combustion: 1971-2003. Paris: IEA Publications.
30.
IMF. 2015. How Large Are Global Energy Subsidies? International Monetary Fund
Working Paper – WP/15/105. Available at: https://www.imf.org/external/pubs/ft/wp/2015/wp15105.pdf.
31.
Jacobsen P., F. Racioppi, F. Rutter. 2009.
„Who owns the roads? How motorised transport discourages walking and
cycling”. Injury Prevention 15:
369-373.
32.
Jacyna M. 1998. “Some aspects of
multicriteria evaluation of traffic flow distribution in a multimodal
transport corridor”. Archives of
Transport 10(1-2): 37-52.
33.
Jacyna M., J. Merkisz. “Proecological
approach to modelling traffic organization in national transport system”.
Archives of Transport 2(30): 43-56.
34.
Jarboui Sami, Pascal Forget, Younes
Boujelbene. 2012. „Public road transport efficiency: a literature review
via the classification scheme”. Public
Transport 4: 101-128.
35.
Kuramochi T., N. Höhne, M. Schaeffer, J.
Cantzler, B. Hare, Y. Deng, S. Sterl, M. Hagemann, M. Rocha, P.A. Yanguas
Parra, G-U-R Mir, L. Wong, T. El-Laboudy, K. Wouters, D. Deryng, K. Blok.
2018. „Ten key short-term sectoral benchmarks to limit warming to
1.5°C”. Climate Policy 18(3):
287-305. DOI: https://doi.org/10.1080/14693062.2017.1397495.
36.
Maibach E., L. Steg, J. Anable. 2009.
„Promoting physical activity and reducing climate change: Opportunities
to replace short car trips with active transportation”. Preventive Medicine 49: 326-327.
37.
Marsden G., T. Rye. 2010. „The
Governance of Transport and Climate Change”. Journal of Transport Geography 18: 669-678.
38.
Marshall S. 2003. “The Street:
Integrating Transport and the Urban Environment”. In: Hensher D.A.,
Button K.J. (eds). Handbooks in Transport
4: Handbook of Transport and the Environment. Elsevier. P. 771-786.
39.
Merven B., A. Stone, A. Hughes, B. Cohen.
2012. Quantifying the Energy Needs of the Transport
Sector for South Africa: A Bottom-Up Model. Energy Research Centre,
University of Cape Town. Available at: http://www.erc.uct.ac.za/sites/default/files/image_tool/images/119/Papers-2012/12-Mervenetal_Quantifying_energy_needs_transport%20sector.pdf.
40.
Mickevicius T., S. Slavinskas, S. Wierzbicki,
K. Duda. 2014. „The effect of diesel-biodiesel blends on the performance
and exhaust emissions of a direct injection off-road diesel engine”. Transport 29(4): 440-448.
41.
Mikulski M., S. Wierzbicki, M. Smieja, J.
Matijosius. 2015. „Effect of CNG in a fuel dose on the combustion process
of a compression-ignition engine”. Transport
30(2):
162-171.
42.
Molotsoane R. 2019. South Africa’s
Climate Change Near-term Priority Flagship Programmes. Paper presented at the
Human Settlements Round Table on Innovation and Transformative Technologies,
The Canvas Riversands – Fourways, South Africa, 29 May.
43.
NCCR. 2011. “Key Mitigation Sector
– Transport”. Available at: http://www.climateresponse.co.za/home/gp/5.6.
44.
Olojede O., A. Yoade, B. Olufemi. 2017.
„Determinants of Walking as an Active Travel Mode in a Nigerian
City”. Journal of Transport &
Health 6: 327-334. DOI: https://doi.org/10.1016/j.jth.2017.06.008.
45.
Pooley C.G., D. Horton, G. Scheldeman, M.
Tight, H. Harwatt, A. Jopson, T. Jones, A. Chisholm, C. Mullen. 2012.
„The Role of Walking and Cycling in Reducing the Impacts of Climate
Change”. In: Ryley T., Chapman L. (eds). Transport and Climate Change. Transport and Sustainability 2: 175-195. Bingley: Emerald Group
Publishing Limited. DOI: http://dx.doi.org/10.1108/S2044-9941(2012)0000002010.
46.
Potter S. 2003. „Transport Energy and
Emissions: Urban Public Transport”. In: Hensher D.A., K.J. Button
(eds). Handbooks in Transport 4: Handbook
of Transport and the Environment. Elsevier. P. 247-262.
47.
PPMC 2017. Proposal for a Transport Decarbonization Alliance (TDA). Draft for
Discussion, March. Available at:
http://Transport-Decarbonization-Alliance-Proposal-2017-03-17-.pdf.
48.
Pucher J., J. Dill, S. Handy. 2010.
„Infrastructure, Programs and Policies to Increase Bicycling: An
International Review”. Preventive
Medicine 50 (Suppl. 1): S106-S125.
49.
Rakhmangulov A., A. Sladkowski, N. Osintsev.
2017. „Green Logistics: Element of the Sustainable Development
Concept. Part 1”. Nase More 64(3): 120-126. ISSN:
0469-6255. DOI: 10.17818/NM/2017/3.7.
50. Rayner S. 2012. International
Experience and Trends: Vehicle Fuel Economy, Taxation and Fuel Quality.
Available at: http://staging.unep.org/transport/pcfv/PDF/GFEI_AfricaLaunch/InternationalExperience.pdf.
51.
RSA 2010. Reducing
Greenhouse Gas Emissions: The Carbon Tax Option. Pretoria: National
Treasury.
52.
Schmidt Marie, Stefan Voss. 2017.
„Advanced systems in public transport”. Public Transport 9(1-2) Special Issue: 3-6.
53.
SDSN, IDDRI. 2014. Pathways to Deep Decarbonization. Interim Report 2014, South Africa
Chapter. SDSN & IDDRI. Available at: http://deepdecarbonization.org.
54.
U.S. Energy Information Administration. 2013.
South Africa: Country Analysis –
Brief Overview. Available at: http://www.eia.gov/countries/country-data.cfm?fips=SF.
55.
van der Post J. 2017, March 28. “You'll
never guess how many vehicles are registered in SA’. Wheels24. Available at: https://www.wheels24.co.za/News/Industry_News/youll-never-guess-how-many-vehicles-are-registered-in-sa-20170328.
56.
Villanueva K., B. Giles-Corti, G. Mccormack. 2008. ”Achieving 10,000 Steps:
A Comparison of Public Transport Users and Drivers in a University
Setting”. Preventative
Medicine 47: 338-341.
57. Vosper S.J., J.F. Mercure.
2016. „Assessing the Effectiveness of South Africa’s Emissions
Based Purchase Tax for Private Passenger Vehicles: A Consumer Choice Modelling
Approach”. Journal of Energy in Southern Africa 27(4). DOI: https://doi.org/10.17159/2413-3051/2016/v27i4a1436.
58.
Western Cape Department of Environmental
Affairs and Development Planning. 2018. Western
Cape Climate Change Response Strategy 2nd Biennial Monitoring and Evaluation
Report 2017/18. Progress in preparing for climate change. March. Cape Town:
Western Cape Department of Environmental Affairs and Development Planning.
59.
Wheels24. 2019. „SEE: Here's how many
cars are set to be sold in SA this year”. Available at: https://www.wheels24.co.za/News/SA_vehicle_sales/see-heres-how-many-cars-are-set-to-be-sold-in-sa-this-year-20190110.
60.
World Bank. 2012. World Development
Indicators Online Database. Washington, DC: World Bank. Available at: http://documents.worldbank.org/curated/en/270671478809724744/pdf/110137-WP-PUBLIC-ECRAI-Transport-CLEAN-WEB.pdf.
61.
World Economic Forum. 2019, February 21. The
Netherlands is paying people to cycle to work. Available at: https://www.weforum.org/agenda/2019/02/the-netherlands-is-giving-tax-breaks-to-cycling-commuters-and-they-re-not-the-only-ones/.
62.
WWF. 2016. Transport Emissions in South Africa. Available at:
http://wwf_2016_transport_emissions_in_south_africa.pdf.
Received 09.08.2020; accepted in revised form 10.10.2020
Scientific
Journal of Silesian University of Technology. Series Transport is licensed
under a Creative Commons Attribution 4.0 International License
[1]
Human Settlement Unit, Research Directorate, Mangosuthu University of
Technology, Umlazi KwaZulu-Natal, South Africa. Email: olojedeo@oauife.edu.ng.
ORCID: https://orcid.org/ 0000-0003-2070-0402