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Who will bell the cat? On the environmental and sustainability risks of electric vehicles

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Transportation Research Part A
journal homepage: www.elsevier.com/locate/tra
Who will bell the cat? On the environmental and sustainability
risks of electric vehicles
Francisco J. Bahamonde-Birke
Sociale Geografie en Planologie, Universiteit Utrecht, Netherlands
I have been confronted recently with many papers considering the triggers and obstacles favoring and/or hampering the adoption
of electric vehicles (EVs). The large majority of these papers include claims such as … “Compared with traditional gasoline vehicles, EVs
have several societal and environmental benefits such as reduce carbon emissions, enhance energy security and promote the usage of renewable
and clean energy” (Wang et al., 2018) or … “These policies are in essence aiming to change the societal norm of fossil fuel based internal
combustion vehicles into a new norm of fuel efficient EVs via a number of push and/or pull measures.” (Nordlund et al., 2018) or … “Plug-in
electric vehicles are seen as a promising option to reduce oil dependency, greenhouse gas emissions, particulate matter pollution, nitrogen oxide
emissions and noise caused by individual road transportation” (Ensslen et al., 2018), just to mention some published in this journal
during in the past year. However, the number of similar cases in the transportation literature is countless.
While I certainly do not want to criticize the quality of the work on adoption of new powertrain technologies that is the actual
content of these papers, I want to raise awareness about the suitability of electric vehicles to actually contribute to sustainability.
Nowadays, and in line with the expectations of the press, politicians and the general public, many researchers take as God-given
that the switch from conventional vehicles to new powertrain technologies, such as EVs, constitutes a big step towards the dec-
arbonization and sustainability of transport systems. Nevertheless, and in spite of its broad acceptance, this is not necessarily true. It
is not even necessarily true when the electrical grid includes a large share of renewable energies; the impact of EVs must be analyzed
on case by case basis.
In countries such as Norway, Iceland or Costa Rica, where almost 100% of the electricity is generated from renewable sources
with a substantial reservoir capacity (i.e. the electric generation can easily follow the demand; Kroposki et al., 2017), EVs are almost
carbon neutral. In any other case, however, it is necessary to consider the impact of an additional vehicle-kilometer on the total
amount of CO
2
emissions associated with the electric grid.
1
The German case constitutes a good example of this phenomenon: Germany is a pioneer of the energy transition (German
Energiewende) and its electric grid exhibits a large amount of renewable sources. However, the electric grid has high volatility (which
arises mostly from wind and solar energy) and cannot easily adapt to follow demand. Hence, the electric generation exhibits large
fluctuations and while at some point the entire demand can be satisfied with wind and solar energy only, at many points every
additional kWh is being generated using lignite (a very CO
2
-intensive energy source). Therefore, charging EVs during those time
periods necessarily implies that the total amount of energy being generated using lignite in the system has to be increased in the same
amount of the energy demanded by the EVs, with disregard of the average amount of renewable sources in the mix (Jochem et al.,
2015).
Consequentially, depending on the time when EVs are being charged, a vehicle like a Chevrolet Volt can be associated with only
37 g CO
2
/km, when electricity is generated from renewable sources only (way below conventional vehicles,
2
Plötz et al., 2018) or as
https://doi.org/10.1016/j.tra.2019.12.001
Received 17 July 2019; Received in revised form 6 November 2019; Accepted 2 December 2019
E-mail addresses: bahamondebirke@gmail.com,f.j.bahamondebirke@uu.nl.
1
Note that an adequate assessment requires the analysis of the entire life cycle of vehicles (LCA), but it largely escapes the scope of this research
note focused on the impact of electricity generation on the ecological performance of EVs. The reader is referred to Messagie (2014),Manzetti and
Mariasiu (2015), and Holmberg and Erdemir (2019) for a detailed review on LCA.
2
For comparison purposes, comparable vehicles (average C-segment) are associated with 139 g CO
2
/km for Diesel vehicles and 151 g CO
2
/km for
Petrol vehicles (KBA, 2019).
Transportation Research Part A 133 (2020) 79–81
Available online 29 January 2020
0965-8564/ © 2020 The Author. Published by Elsevier Ltd. This is an open access article under the CC BY-NC-ND license
(http://creativecommons.org/licenses/BY-NC-ND/4.0/).
T
much as 190 g CO
2
/km, when electricity is generated from lignite (way above conventional vehicles
2
,Plötz et al., 2018). Fur-
thermore, given the charging patterns of EVs, the large majority of the electric charge occurs during the evenings (Anderson et al.,
2018).
3
During those time periods, the contribution of renewable energies is low and the electric demand is high (Schill and
Gerbaulet, 2015), meaning that the electricity being generated to satisfy the demand mostly comes from lignite (i.e. 190 g CO
2
/km);
in fact, Schill and Gerbaulet (2015) show that replacing conventional vehicles by electric vehicles increases the CO
2
emissions
throughout the country. Helveston et al. (2015) and Jenn et al. (2019) report similar results for China and the US.
It is also important to note that it is not adequate to associate the use of EVs with the average CO
2
emissions of the grid, as it does
not reflect the emissions associated with the generation of the energy actually used by the vehicle (which is obviously equal or larger
than the average given that the marginal emissions are increasing). Or in other words, associating EVs with the average CO
2
emissions of the grid implies assuming that the same electricity mix can be used to generate additional energy (for EVs), which is
obviously not possible when no further renewable sources are available (and every additional kWh would have to be generated using
less environmentally friendly sources). Consequentially, doing so incorrectly associate EVs with lower CO
2
emissions than the amount
actually being required to generate the electricity (which is reflected by the marginal emissions).
Similarly, it is also incorrect to state that EVs exhibit a better ecological performance than conventional vehicles when CO
2
emissions cap-mechanisms - like the European Union’s emissions trading system (EU ETS) - are set in place. Under these circum-
stances, the analyst would rather be capturing the effect of imperfect regulation (which may or may not be improved in the short/
medium term – note that is perfectly possible to include conventional vehicles into systems like EU ETS via fuel taxes) and not an
actual difference in the ecological performance of EVs relative to their conventional counterparts. Hence, ceteris paribus (and con-
sidering equal regulation on greenhouse pollutants for all alternatives) it would still be more efficient to rely upon vehicles with less
marginal emissions (e.g. compensating the CO
2
emissions of conventional vehicles via carbon credits produces the same results as
replacing the conventional vehicles by EV at a lesser cost). Along these lines, it must also be pointed out that the reach of mechanisms
like the EU ETS and the possibilities of compensating CO
2
emissions are also not unlimited and a large increase in CO
2
emissions
would put a lot of pressure on the system, as steep increases in the price of emissions permits have been observed every time the EU
ETS has expanded (Hintermann, 2017). In fact, the transport sector currently represents 25% of the total CO
2
emissions in the area
covered by the EU ETS (Eurostat, 2019) and the EU ETS covers 42% of those emissions (Hintermann, 2017); hence, including the
transport sector would result in an increase of ca. 60% of the emissions to be accommodated under the cap, and this figure will be
much larger if conventional vehicles are replaced by vehicles with higher marginal emissions.
The purpose of this note, however, is not to hamper the transition towards electromobility. I acknowledge the benefits of EVs in
countries like Norway or Iceland; I also acknowledge the benefits of EVs in terms of local emissions (which may prove highly
important in overly polluted cities), and also eventual benefits of EVs to balance the grid by taking advantage of their batteries when
surplus in the generation occurs. This, however, does not change the fact that, under current conditions and with flat energy prices, a
substantial increase in the number of EVs in many countries would necessarily result in an increase of CO
2
emissions. Luckily, many
European countries are not going to meet their goals regarding the number of EVs on the street by 2020, as their current electric grids
and regulation (e.g. lack of incentives to charge vehicles during generation surpluses) are not prepared. Hence, it would result either
in an important increase in greenhouse gas emissions or in prohibitively high CO
2
permit prices, compromising mechanisms such as
the EU ETS.
4
The actual purpose of this note is to raise awareness among authors and reviewers regarding the risks associated with replacing
conventional vehicles - especially those highly efficient in terms of CO
2
emissions, such as Diesel or LPG vehicles - by electric vehicles
(especially if not appropriate incentives to take advantages of generation surpluses are set in place). Despite the fact that the evidence
I am summarizing is not new (and most of it has been published in this very journal), a large proportion of the scientific community
seems to be daunted by the hype around the benefits of EVs and are unwittingly neglecting their risks. It is our duty as scientific
community to raise awareness about these issues and not let ourselves go with the hype.
Appendix A. Supplementary material
Supplementary data to this article can be found online at https://doi.org/10.1016/j.tra.2019.12.001.
References
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3
Actually, Anderson et al. (2018) show that the amount of renewable sources is enough to satisfy the electricity demand for a fleet of 6 million EVs
in 2030 regardless of the time of the day (accounting for the electricity grid energy composition in 2030). However, if the renewable sources are not
enough to satisfy the entire electric demand in the system (i.e. not just the transportation sector), the additional demand associated with EVs would
necessarily have to be satisfied by increasing the total generation using fossil sources (i.e. lignite).
4
Note that this stands even when countries aim at greener electricity grids in the long-term. If so, there will be an optimal time window for a large-
scale transition towards EVs (from a CO
2
emissions perspective and taking incentives schemes to charge EVs during generation surpluses into
account). This will not hamper the development of the technology as a large-scale introduction of EVs is already reasonable in other countries.
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A well-known result about market power in emission permit markets is that efficiency can be achieved by full free allocation to the dominant firm. I show that this result breaks down when taking the interaction between input and output markets into account, even if the dominant firm perceives market power in the permit market alone. I then examine the empirical evidence for price manipulation by the ten largest electricity firms during phase I of the EU ETS. I find that some firms’ excess allowance holdings are consistent with strategic price manipulation, and that they cannot be explained by price speculation or by precautionary purchases to insure against uncertain future emissions. My results suggest that market power is likely to be an empirically relevant concern during the early years of emission permit markets.
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Abstract We analyze the impacts of future scenarios of electric vehicles (EVs) on the German power system, drawing on different assumptions on the charging mode. We find that the impact on the load duration curve strongly differs between charging modes. In a fully user-driven mode, charging largely occurs during daytime and in the evening, when power demand is already high. User-driven charging may thus have to be restricted because of generation adequacy concerns. In contrast, cost-driven charging is carried out during night-time and at times of high PV availability. Using a novel model formulation that allows for simulating intermediate charging modes, we show that even a slight relaxation of fully user-driven charging results in much smoother load profiles. Further, cost-driven EV charging strongly increases the utilization of hard coal and lignite plants in 2030, whereas additional power in the user-driven mode is predominantly generated from natural gas and hard coal. Specific CO2 emissions of EVs are substantially higher than those of the overall power system, and highest under cost-driven charging. Only in additional model runs, in which we link the introduction of EVs to a respective deployment of additional renewables, electric vehicles become largely CO2-neutral.
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Electric and hybrid vehicles are associated with green technologies and a reduction in greenhouse emissions due to their low emissions of greenhouse gases and fuel-economic benefits over gasoline and diesel vehicles. Recent analyses show nevertheless that electric vehicles contribute to the increase in greenhouse emissions through their excessive need for power sources, particularly in countries with limited availability of renewable energy sources, and result in a net contribution and increase in greenhouse emissions across the European continent. The chemical and electronic components of car batteries and their waste management require also a major investment and development of recycling technologies, to limit the dispersion of electric waste materials in the environment. With an increase in fabrication and consumption of battery technologies and multiplied production of electric vehicles worldwide in recent years, a full review of the cradle-to-grave characteristics of the battery units in electric vehicles and hybrid cars is important. The inherent materials and chemicals for production and the resulting effect on waste-management policies across the European Union are therefore reported here for the scope of updating legislations in context with the rapidly growing sales of electric and hybrid vehicles across the continent. This study provides a cradle-to-grave analysis of the emerging technologies in the transport sector, with an assessment of green chemistries as novel green energy sources for the electric vehicle and microelectronics portable energy landscape. Additionally, this work envisions and surveys the future development of biological systems for energy production, in the view of biobatteries. This work is of critical importance to legislative groups in the European Union for evaluating the life-cycle impact of electric and hybrid vehicle batteries on the environment and for establishing new legislations in context with waste handling of electric and hybrid vehicles and sustain new innovations in the field of sustainable portable energy. Full and free access to article until September 12, 2015 at following link: http://authors.elsevier.com/a/1RQ1z4s9HvhLnn