Consider, for example, light- and medium-duty vehicles. The price of a new
EV is on track to fall below that of comparable conventional internal
combustion engine vehicles during this decade. This price decline is driven
by the ongoing, remarkable decline in battery prices, manufacturers’
increasing experience in producing EVs, and improved battery technologies
on the horizon. Moreover, EVs are less expensive to operate and maintain
than conventional vehicles.
But the transition to EVs is not a sure thing, and in any event it can be expedited and supported by policy. In particular,
the chicken-and-egg externality of charging stations poses some significant challenges. Absent
adequate slow (level 2) charging stations, EV owners must provide their own
charging capacity—which means a dedicated parking space where they are able
to install a charger. Not surprisingly, EV purchases heavily skew toward
higher-income families with their own garages, which in turn affects the
types of EVs produced. Policy to support reliable widespread overnight or
at-work charger availability could help overcome this chicken-and-egg
problem, thereby accelerating the transition and ensuring a larger EV
share.
On the other hand, a moderate carbon tax is likely to have little effect on
EV purchases, because the cost impact is small (a $40/ton carbon tax
implies $0.36 for a gallon of gasoline). In fact, there is a substantial
literature that investigates whether car buyers properly take into account
fuel prices when they purchase a vehicle; that literature tends to find
that purchasers only partially account for fuel prices. For light- and
medium-duty vehicles, addressing the network externalities and innovation
externalities for advanced batteries is more effective and impactful than
carbon pricing. Because those policies aim to facilitate the transition
from the current low-EV equilibrium to a stable, low-cost high-EV
equilibrium, those transitional policies have a limited duration and
one-time costs.
In contrast, aviation is a major and growing source of carbon dioxide
emissions and appears quite difficult to decarbonize. Currently there is
enthusiasm about low-carbon sustainable aviation fuel. Such fuel can be
produced through conventional pathways such as conversion of waste
vegetable oils and oil crops to renewable jet fuel or through advanced
pathways—for example low- or negative-carbon alcohols, such as ethanol from
energy grasses, converted to jet fuel.
In its 2021 Annual Energy Outlook, however, the US Energy
Information Administration projected the price of petroleum jet fuel to be
$2.77/gallon in 2050 (2020 US dollars). The prospect of sustainable
aviation fuel competing with petroleum jet fuel at $2.77/gallon, unaided by
an implicit or explicit carbon price, is daunting. A switch to sustainable
fuel depends on robust funding to address the innovation externality and,
when those fuels become available at scale, a high carbon price (either an
explicit price or a clean fuel standard for aviation). Especially if the
carbon price is implemented through an aviation fuel standard, this phasing
could be critical: implementing a fuel standard too soon runs the risk of
preferencing first-generation fuels without adequate support for scalable
fuels with zero or negative carbon footprints, as has been seen in the
failure of the US Renewable Fuel Standard to promote second-generation
low-carbon ethanol. Sustainable aviation fuel works in standard jet engines
and uses much the same infrastructure as petroleum jet fuel, so network
externalities matter less. For aviation, this suggests policy that strongly
supports the development and commercialization of advanced, scalable, and
truly low-carbon sustainable aviation fuel now and a credible commitment to
a high sectoral carbon price in the future.
In the power sector, all three externalities figure prominently in the
transition. In the United States, new wind and solar power generation is
less expensive than coal and natural gas in some but not all parts of the
country. As a result, US power sector modeling suggests that a national
policy that effectively puts a price on carbon—such as a clean electricity
standard—is necessary to achieve substantial near-term decarbonization, say
80 percent by 2030. Deeper decarbonization will likely require significant
innovation-driven cost reductions in storage technologies. In addition, the
infrastructure of the US power sector restricts the ability to transmit
green electricity from regions with high renewable resources to demand
centers.
The power sector also faces serious institutional challenges, such as the
regulatory and physical ability to use time-of-day pricing and load
management and the institutional and political problems of siting new
transmission capacity. For the power sector, supporting research and
development of long-term storage technologies and addressing multiple
infrastructure and institutional limitations are essential. The necessary
first step, however, is a sectoral policy, such as a clean electricity
standard, that has the effect of placing a price on carbon.
This is not to say that an economy-wide carbon tax is undesirable: the
decarbonization from a clean electricity standard, and its limited effect
on power prices, could be accomplished by an economy-wide carbon tax
combined with government subsidies for renewable power, and that tax would
yield some decarbonization from other sectors as well. For aviation, an
economy-wide carbon price could, two decades from now, support the use of
still-expensive low- or zero-carbon alternatives to petroleum jet fuel. But
this reasoning suggests that pursuing an economy-wide carbon price is a
lower priority today than it was when it was expensive to be green.
Economy-wide carbon pricing, while desirable, by itself is neither
efficient nor, at politically plausible prices, sufficient to drive deep
decarbonization.