ArticlePDF Available

Dedicated climate ministries help to reduce carbon emissions

Authors:

Abstract and Figures

Several countries have introduced dedicated national climate ministries in the last two decades. However, we know little about the consequences of these ministries. We demonstrate that the introduction of climate ministries helps to reduce carbon emissions. A difference-in-differences analysis of a global sample of countries reveals robust and statistically significant evidence that introducing a dedicated climate ministry lowers carbon emissions substantially. At the same time, establishing such climate ministries does not significantly influence the introduction of new climate policies. This indicates that climate ministries primarily amplify climate action by improving the effectiveness of the governmental measures taken rather than by increasing the number of climate policies themselves.
Content may be subject to copyright.
npj | climate action Article
https://doi.org/10.1038/s44168-024-00147-9
Dedicated climate ministries help to
reduce carbon emissions
Check for updates
Julian Limberg 1, Yves Steinebach 2&JacobNyrup 2
Several countries have introduced dedicated national climate ministries in the last two decades.
However, we know little about the consequences of these ministries. We demonstrate that the
introduction of climate ministries helps to reduce carbon emissions. A difference-in-differences
analysis of a global sample of countries reveals robust and statistically signicant evidence that
introducing a dedicated climate ministry lowers carbon emissions substantially. At the same time,
establishing such climate ministries does not signicantly inuence the introduction of new climate
policies. This indicates that climate ministries primarily amplify climate action by improving the
effectiveness of the governmental measures taken rather than by increasing the number of climate
policies themselves.
To effectively combat escalating climate change, governments must take
decisive action to substantially reduce greenhouse gas emissions. In recent
times, the discourse has shifted from the question of how to achieve inter-
national cooperation to the question of how to design national public
institutions to foster climate actions17. Specically, the role of establishing
dedicated climate ministries has risen to the forefront of this scholarly
debate8,9. Dedicated climate ministries are considered potential catalysts for
driving comprehensive and concerted efforts toward climate action. The
main argument is that climate ministries come with clearer responsibilities
and increased administrative resources dedicated to addressing the issue of
climate change.
Despite these supposed advantages of dedicated climate ministries,
empirical evidence regarding their actual impact on climate policy ambi-
tions and effectiveness remains scarce. We address this research gap by
examining a comprehensive sample of 169 countries over a span of two
decades (2000 to 2021). We use a difference-in-differences (DiD) design to
investigate whether establishing a dedicated climate ministry makes a dif-
ference in terms of the quantity, type, and effectiveness of climate policies.
We compare countries that have introduced a dedicated climate ministry to
those that have not. Our analysis reveals that the establishment of dedicated
climate ministries contributes to a reduction in carbon emissions. Yet, it
does not signicantly inuence the introduction of new climate policy
legislation. Instead, variations in carbon emissions appear to be driven
largely by the enhanced effectiveness in the implementation and enforce-
ment of existing climate policies.
The paper is structured as follows: First, we discuss the purported
advantages of climate ministries in addressing climate change. Next, we
conduct a comprehensive mapping of existing climate ministries and ana-
lyze the impact of their introduction on carbon emissions. Furthermore, we
assess the mechanisms that link the establishment of a dedicated climate
ministry with carbon emission reduction. Thereafter, we discuss our results.
The nal chapter presents our research design and methodologies.
The benets of dedicated climate ministries
Dedicated climate ministry come with two central benets. The creation of a
dedicated climate ministry helps to ensure clear lines of responsibility5,10.
Moreover, the creation of a dedicated climate ministry guarantees that
specic administrative resources, in terms of both staff and budget, are
allocated to addressing climate change issues. These advantages can enhance
climate action through different mechanisms.
First, governments can leverage such specialized ministries to
reduce CO
2
emissions through policy formulation. This can be achieved
through the proliferation of more, stricter, or better designedpolicies.
A climate ministry crystallizes accountability, clearly delineating the
responsibility for initiating and steering climate actions. In government
structures without a dedicated climate ministry, climate-related policy
responsibilities are often spread across various ministries or depart-
ments, such as those dealing with energy, environment, or industry11.It
is thus often unclear who (exactly) needs to take the measures it needs to
tackle climate change. In addition, even though comprehensive climate
action still requires the collaborative effort of various government sec-
tors, a climate ministry can drive cross-ministerial coordination, com-
pelling other departments to take necessary steps12. Moreover, the
augmented administrative capacities that come with climate ministry
can empower governments to formulate more and betterpolicies. As
emphasized by Fernández-i-Marín et al., the creation of well-designed
policies is not a straightforward task it requires a substantial level of
administrative capacity13. The establishment of a climate ministry, with
its focused mandate and specialized workforce, can signicantly con-
tribute to the development and execution of these policies.
1Kings College London, London, Great Britain. 2University of Oslo, Oslo, Norway. e-mail: yves.steinebach@stv.uio.no
npj Climate Action | (2024) 3:70 1
1234567890():,;
1234567890():,;
Second, climate ministries play a pivotal role in enhancing the
effectiveness of a countrys climate policy through better enforcement
and implementation practices. Climate ministers typically do not
implement policies directly but delegate this task to governmental
agencies or administrative bodies situated at different levels of
government14. A key insight from the policy implementation literature
is that during this process, things might not transpire as intended, since
other levels of government might, for various reasons, fail to take the
requisite action to render a policy effective. These reasons can include
conicting priorities, lack of clear guidance or insufcient expertise,
political opposition, or challengesincoordinationandcommunication
across the multiple agencies involved15. Equipped with dedicated
workforces and nancial resources, a climate ministry can monitor
various enforcement agencies to ensure they are executing policies as
intended and assist subordinate levels of government in adhering to
climate objectives. Steinebach, for instance, nds that clean air policies
are more effective in reducing air pollutant emissions when the
implementation process is overseen by a specialized central ministry16.
Figure 1summarizes these theoretical considerations.
Mapping dedicated climate ministries
Figure 2presents the number of countries with a dedicated climate ministry
over time. The rst ministry portfolio carrying climatein the organiza-
tional title was the Minister of Climate Change Issuescreated in New
Zealand in 2005. Of the 38 countries that have introduced a climate ministry
at some point in time, 30 still had a ministry in 2021. Interestingly, in only
ve countries, these ministries were solely responsible for climate matters. In
most instances, the portfolio of these climate-centric ministries was merged
with at least one other policy domain, typically either environmentor
energy.
Looking at the geographical distribution of climate ministries
(Fig. 3), we can see that starting with Belgium and Denmark in 2007,
many European countries have introduced dedicated climate min-
istries in the last two decades. However, climate ministries are not
exclusively a Western phenomenon. Several countries in the Global
SouthsuchasGabon,India,andPapuaNew Guinea have established
climate ministries as well (see also Fig. S1 in the Supplementary
Material).
Climate ministries and carbon emissions
In the next step, we conduct an econometric analysis to identify
whether the introduction of a dedicated climate ministry affects carbon
emissions. As detailed below in the method section, we use a difference-
in-differences design to look at changes in carbon emissions up to 5
years before and after establishing a dedicated climate ministry. We
then compare emission trajectories to countries that have not intro-
duced a climate ministry in the same period and use a matching
technique to only compare countries with similar covariate
trajectories17.
As shown in Fig. 4, our empirical results strongly support dedi-
cated climate ministriesemission-reduction potential. In the year after
the establishment of a ministry, emissions drop on average by more
than 0.36 metric tons per capita (95% condence interval of 0.71 to
0.04 metric tons per capita) compared to countries that have not
introduced a climate ministry. This effect is statistically signicant at
the 5% level and increases further to around 1.06 metric tons per capita
(95% condence interval of 1.87 to 0.29 metric tons per capita)
after 5 years. This effect not only proves to be statistically signicant
but also quite substantial. The emission savings after 5 years equates to
roughly one-eighth (12.5 percent) of the average per capita emissions
in OECD countries. In other words, establishing a climate ministry
substantially reduces carbon emissions. In contrast, emission trajec-
tories do not differ between countries before the establishment of a
dedicated climate ministry. Thus, the parallel trend assumption holds,
i.e., the identied effects on carbon emissions are not a continuation of
diverging emission trajectories prior to the introduction of climate
ministries.
Fig. 1 | Theoretical considerations on the benets of dedicated climate ministries. This gure summarizes the theoretical considerations tested in this paper.
Fig. 2 | Number of countries with a dedicated climate ministry. The gure presents
the number of countries with a dedicated climate ministry over time between 2000
and 2021.
https://doi.org/10.1038/s44168-024-00147-9 Article
npj Climate Action | (2024) 3:70 2
What are the mechanisms driving this emission reduction?
As discussed above, climate ministries can help governments to achieve
emission reductions in different ways. First, by formulating more, more
ambitious, and betterclimate policies. Second, by enhancing the enfor-
cement and application of existing climate policies.
To assess whether the establishment of climate ministries leads to
more climate policies, we take the total number of climate mitigation
policies from the Climate Policy Database18 and use the same econo-
metric difference-in-differences technique to estimate the effect of
dedicated climate ministries on climate policy outputs. The results show
no statistically signicant differences between countries that have
introduced a dedicated climate ministry and those that have not
(Fig. 5, left panel). On av erage countries do not levy more clim ate policies
after establishing a ministry. Furthermore, there are no diverging trends
in climate policy-making prior to the establishment of a climate
ministry. Thus, the emission-reduction effect of establishing a climate
ministry cannot be explained by a simultaneous increase in policies.
Certainly, evaluating the inuence of climate ministries on the overall
count of policies overlooks the distinctions in the various types of policies
that governments can use to address climate change. Governments have an
array of both softand hardclimate policy instruments at their
disposal19,20. Notably, regulatory and market-based instrumentsparticu-
larly carbon trading and taxes are considered more ambitious measures in
climate policy21. However, we do not nd a statistically signicant effect of
climate ministries on these ambitious climate policies either (Fig. 5,middle
panel). On average, countries that established a climate ministry do not have
a statistically higher likelihood of introducing more ambitious regulatory or
market-based climate policies.
Furthermore, it might be the case that the establishment of a climate
ministry leads to better designed policies. Government might make use of a
more diverse range of climate policies to demand-tailor policies to tackle
climate issues. To test this, we look at the impact of the establishment of a
climate ministry on the average instrument diversity (AID) of climate
mitigation policies. This measure, as proposed by Fernández-i-Marín et al.,
measures the policy design quality based on the degree to which govern-
ments use different instruments and instruments combinations across the
various policy targets and sectors they address13. The underlying logic is that
a greater instrument diversity reects a greater effort of the government to
nd tailor-madesolutions to the different policy problems they address.
We do not nd a statistically signicant effect of the establishment of a
climate ministry on instrument diversity (Fig. 5,rightpanel).
We run several additional models to check for the sensitivity of our data
and the accuracy of our model choice. First, we run our models without
using the matching algorithm (Fig. S5), by additionally matching on lea-
dership changes (Fig. S6) as well as on green party government participation
(Fig. S8), and by only looking at ministries where the climate minister is the
head of the ministry (Fig. S7). Findings are robust. Furthermore, instead of
running a difference-in-differences analysis, we test for the inuence of
climate ministries on carbon emission in an ordinary time-series cross-
section-analysis (Table S1). In this analysis, the presence (or absence) of
climate ministries is quantied using a binary dummy variable. Again, our
analysis shows that having a climate ministry is a statistically signicant and
robust predictor of bigger reductions in CO
2
. In the full model that includes
Fig. 3 | Countries that have established a dedicated climate ministry. The world map presents per country the year of the rst establishment of a dedicated climate ministry.
Fig. 4 | Effect of establishing a dedicated climate ministries on CO
2
emissions.
The gure present the effect of establishing a dedicated climate Ministries on per
capita CO
2
emissions. The gray areas show the 95% condence intervals.
https://doi.org/10.1038/s44168-024-00147-9 Article
npj Climate Action | (2024) 3:70 3
various control variables and a lagged dependent variable, CO
2
emissions
per capita decrease by 0.16 metric tons more for each year a country has a
dedicated climate ministry.
In sum, these ndings indicate that introducing a climate ministry does
neither lead to more nor to more ambitious or better-designed policies. This
renders the improved implementation and enforcement of existing climate
policies as the most plausible explanatory factors for the observed differ-
ences. The key argument here is that the clearer delineation of responsi-
bilities and the provision of extra administrative resources within these
ministries improve the governments capacity to supervise the imple-
mentation authorities16.
We probe this argument in three additional analyses. First, we differ-
entiate between specialized and general ministries. We dene general
ministries as those that focus on at least three additional issue areas next to
climatechange,whilemorespecialized ministries are dened as dealing with
a maximum of two additional issues. The heterogeneity of ministries
portfolios should come at the cost of undermining the observed effects on
improved implementation as responsibility gets blurred and additional
(specialized) administrative resources are less plentiful8.Inlinewiththis
theoretical expectation, we do not nd any effect of these ministries that deal
with climate as one of several topics on carbon emissions (Fig. S2 left panel).
In contrast, we do nd a strong effect of establishing a more specialized
climate ministry (Fig. S2 right panel).
Second, we look at the effect of general environmental ministries on
carbon emissions. In contrast to climate ministries, environmental minis-
tries are not solely focused on climate action but typically deal with various
topics such as air pollution in general, water pollution and nature con-
servation. Using the same econometric technique, we nd no robust sta-
tistically signicant effect of establishing a general environmental ministry
on carbon emissions per capita (Fig. S3). This further supports the argument
that the specialization of dedicated climate ministries is key for reducing
carbon emissions.
Finally, we check whether the effect of having a climate ministry varies
between countries. In line with our arguments about the importance of
implementation effectiveness, we would expect that new climate ministries
are less likely to improve policy implementation in countries with lower
overall state capacity. In other words, a lack of general state capacity
undermines the effect of establishing new institutional structures. Over-
coming disjointed responsibilities and making sure additional resources are
usedforimplementationpurposesisharderwhenthestategenerallylacks
power and authority. This is well in line with previous research indicating
that general state capacity is a crucial determinant of a countrys capability to
build up more effective administrative structures to tackle climate change22.
We test for heterogenous treatment effects in two ways. First, we re-run
the previous analyses but leave out individual countrie stha t have established
a dedicated climate ministry. The effect of climate ministries on emission
after 5 years stays robust (Fig. S4). This ensures that our ndings are not
driven by extraordinary emissionreductionsinspecic countries. The
analysis further indicates that the observed effect on CO
2
becomes markedly
stronger when excluding countries with particularly low state capacity, such
as India, Oman, Gambia, Zimbabwe, and Papua New Guinea. Given that
these states may encounter more signicant challenges in establishing
effective administrative structures, despite potentially having the best
intentions, this nding reinforces our assertion that the creation of climate
ministries does indeed make a difference by enhancing administrative
capacities.
Second, we make use of the time-series cross-sectional analysis pre-
sented. This econometric set up allows us to conduct a statistical test which
checks whether the effect of having a climate ministry varies by overall state
capacity. To do this, we run a model with an interaction effect. More pre-
cisely, we use the full Model 4 in Table S1 and expand it by interacting the
climate dummy with generate a general state capacity index developed by
Hanson and Sigman23 who use Bayesian latent variable analysis covering a
wide range of indicators related to different state capacity dimensions. To
interpret the interaction effect, we present marginal effect plots24.Further-
more, we add a histogram to the plot and use a binning estimator developed
by Hainmueller et al.25. The estimator splits the data into three different bins
(high, medium, low) and estimates whether the effect of having a climate
ministry varies between the different bins. As shown in Fig. 6,ourresults
show that the effect of a climate ministry on carbon emissions is sub-
stantially stronger for countries with overall higher levels of state capacity. In
contrast, the effect is indistinguishable from zero in countries with lower
levels of state capacity. In sum, these ndings show support for our argu-
ment about the crucial role of climate ministries in enhancing the effec-
tiveness of climate policy. In countries with substantive state capacity,
climate ministries help to lower emissions substantially, while lacking state
capacity undermines the mechanism of increased implementation effec-
tiveness fundamentally.
It is important to emphasize that our ndings substantially dismiss
the notion that the observed impacts of climate ministries are merely a
by-productof an overarching rise in governmental climate ambitions.
If the creation of these ministries were simply a reection of an under-
lying process of increased governmental commitment towards climate
action, we would expect to see ministry formation going hand in hand
with adopting more, or more ambitious, policies. Similarly, given the
absence of a trend before the creation of a climate ministry, we can rule
Fig. 5 | Effect of establishing a dedicated climate ministries on climate policies. The gure present the effect of establishing a dedicated climate ministries on the number of
the adopted policies; the number of ambitious adopted policies; and the average instrument diversity.
https://doi.org/10.1038/s44168-024-00147-9 Article
npj Climate Action | (2024) 3:70 4
out the possibility that climate ministries are establ ished as a reaction to a
signicant surge in climate policies. Instead, our evidence suggests that
climate ministries do have their own and tangible impact on policy
outcomes, independent of the broader (previous) governmental initia-
tives or ambitions.
Likewise, one might contend that the observed effects are not
attributable to enhanced enforcement, but rather to the signaling
effect of the statescommitment.Forinstance,BayerandAklin
26 have
shown that the rollout of the EU Emissions Trading Scheme (ETS)
impacted businessesbehavior, even when carbon prices were
insufciently high to drive tangible changes in carbon emission levels.
The authors conclude that the very establishment of a formal climate
policy framework was enough to bolster the perception of the gov-
ernments resolution among businesses, prompting them to begin
reducing their emissions. The same could be true for climate ministry
creation. Certainly, we cannot completely discount the possibility
that a portion of the emission reductions observed may stem from a
reaction by the targeted groups that is entirely disconnected from the
actual climate policies or their enforcement. Nevertheless, we con-
sider the argument for improved policy implementation to be more
compelling. This is for two reasons: First, if the impact were merely
attributable to signaling,then the specicity of the term climate
being used in isolation or in conjunction with other terms should not
yield a markedly different outcome (see again our discussion on the
level of specializationof climate ministries). In both scenarios, the
signal sent by the governmentits professed priority of addressing
climate concernsis essentially the same. Second, if it were merely
about signaling, with the government failing to take substantive
action thereafter, we would expect to observe a more abrupteffect
that potentially fades as citizens and businesses come to realize that
the governments intentions are not followed by concrete measures.
However, what we observe is quite the contrary; the impact steadily
grows stronger over time, suggesting that there is indeed realaction
underpinning these changes.
Discussion
The challenging task of addressing climate change demands careful coor-
dination and a comprehensive transformation of existing institutional
arrangements. Our research into the establishment of dedicated climate
ministries offers important insights into the concrete ways in which insti-
tutional change can bolster climate action. Our empirical ndings suggest
that creating designed climate ministries leads to signicant reductions in
carbon emissions. This is pivotal, considering that a drop in carbon emis-
sions is a direct metric reectingthetangibleimpactofclimatepolicies.This
positive outcome becomes even more noteworthy when we consider that
this reduction is achieved without a simultaneous increase in the number or
stringency of climate policies.
The presence of a dedicated climate ministry, as indicated by our
analysis, paves the way for a more coherent approach to climate action,
eliminating the potential pitfalls that arise from blurred or disjointed
responsibilities. By ensuring clear demarcation of responsibility and ded-
icating resources specically towards climate policy issues, climate minis-
tries enhance the effectiveness of existing climate policies. This nding
refutes the notion that merely increasing policy numbers or intensifying
ambitiousness is the only path forward. Instead, it underscores the impor-
tance of having a dedicated body with clear responsibilities that can steer
climate action in a focused manner.
Yet, it is equally essential to recognize the limitations and nuances
within this broader observation. As revealed by our supplementary analyses,
mere nomenclature, or the cursory inclusion of climatewithin a ministrys
name is not enough. The real impact comes from a genuine specialization,
where climate action is prioritized and not diluted amidst other responsi-
bilities. Our study also throws light on the signicance of having the right
kind of institutional architecture. When climate action is situated within
broader (environmental) ministries, the specicity required for targeted
climate action could be compromised. Thus, while environmental concerns
are undoubtedly paramount, there is a pressing need for focused attention
on climate issues, given the scale and urgency of the climate crisis. In light of
the ndings presented, two straightforward policy recommendations can be
made: First, governments should consider establishing stand-alone minis-
tries with a sole focus on climate change. Second, optimally, these should be
standalone climate ministries, free from the dilution of attention and
resources that often accompanies broader environmental or multi-focus
portfolios.
The formation of dedicated climate ministries and their impact on
carbon emissions presents a compelling argument, revealing the
importance of specialized institutional structures for effective climate
action57. However, the broader ecosystemwithin which these min-
istries operate is characterized by inter-ministerial dynamics and
coalition politics. Both these aspects can profoundly inuence the
effectiveness of climate ministries in practice, and thus, merit closer
examination in future research. First, in any governmental structure,
ministries do not operate in isolation. Their actions, decisions, and
policy formulations often intersect with the mandates of other min-
istries. This intersection can either foster synergies or lead to compe-
tition for resources, policy dominance, or even bureaucratic turf
wars27,28 Future research could further investigate how the effectiveness
of climate ministries is inuenced by the presence (or absence) of other
ministries. Second, the distribution of ministerial portfolios among
coalition partners is a strategic exercise, often reecting the power
dynamics and priorities of the involved parties. It would therefore be
intriguing to explore how the inuence of climate ministries varies, for
instance, based on whether the ministry is led by the senior or the
junior partner in a coalition. Finally, the effect of a climate ministry
might depend on broader socio-economic and political characteristics.
For example, our sensitivity analysis suggests that the effect of estab-
lishing a climate ministry might be stronger in richer countries with
Fig. 6 | Effect of establishing a dedicated climate ministries on climate policies for
different levels of state capacity. The gure present the effect of establishing a
dedicated climate Ministries on per capita CO
2
emissions for different levels of state
capacity. Its plots show the estimated marginal effects using both the conventional
linear interaction model and the binning estimator. The gray areas show the 95%
condence intervals. The histogram shows the distribution of the moderator variable
by differentiating between countries with (red bars) and without (grey bars) a cli-
mate ministry in a respective year.
https://doi.org/10.1038/s44168-024-00147-9 Article
npj Climate Action | (2024) 3:70 5
higher overall administrative capacities. The rapid diffusion of climate
ministries will allow future analyses to have a closer look at factors that
might serve as moderators.
In conclusion, as countries grapple with the urgent task of climate
mitigation, creating dedicated climate ministries stands out as an ac tionable,
impactful step. Coupled with robust execution, these institutional changes
could become pivotal in the global battle against climate change.
Methods
Our analysis relies on panel data for 169 countries between 2000 and 2021,
and a list of countries can be found in the Supplemental Material. Our data is
structured in country-years. Our central independent variable is climate
ministry creation. We then look at the effect of establishing a dedicated
climate ministry on CO
2
emissionsaswellasonthenumber,type,and
design of policies.
We retrieved the ministry names (in English) and the dates of their
creation from the WhoGov dataset. Although the WhoGov dataset is pri-
marily designed to provide bibliographic details such as gender and party
afliation of cabinet members across all countries, it can be restructured to
reveal the names of the organizations these cabinet members helm (Nyrup
& Bramwell 2020). A ministrysportfoliocanbeidentied in two ways: rst,
by dissecting the ministrys structure to understand the subjects its orga-
nizational units handle and, second, by referring to the given name of the
ministry. Therefore, we code a country as having established a dedicated
climate ministry when the word Climateappears in a ministry name for
the rst time. Moreover, we validated all the identied ministries against
secondary sources, and we checked whether there were any ministries not
identied by WhoGov by conducting systematic internet searches.
Although a ministry can hold responsibility for a specicpolicyareaeven
without its name explicitly referencing this area (for discussion, see Klüser,
et al.29), the inclusion of a policy area within a ministrys name substantially
signies its place within the ministrys policy portfolio30.Thenamesof
ministerial portfolios and ministries are not always synonymous. For
example, in New Zealand, the minister for Climate Change operates in the
Ministry for the Environment. To take this into account we rerun the main
analysis in the Appendix (Fig. S7) where we exclude ministries with multiple
ministers.
Policy data were extracted from the Climate Policy Database18.Today,
this database includes over 5000 national climate policies worldwide. The
database conceives of policies as the combination of certain sectors (what is
addressed?) and policy types/instruments (how is it addressed?). The
included sectors encompass Agriculture and Forestry, Buildings, Electricity
and Heat, General, Industry, and Transport. The array of policy instruments
encompasses, among others, economic instruments, information and
education, regulatory instruments, and research & development and
deployment. We specically distinguish between regulatory and market-
based instruments, typically viewed as more ambitious, and other policy
measures. The latter group includes initiatives related to information and
education, research & development and deployment, and voluntary
approaches. Data on CO
2
emissions comes from the World Bank, which
sourced data from the Climate Watch Historical GHG Emissions
Database31.
In our analysis, we also consider a range of different time-variant
variables to ensure a comprehensive examination of the relationships at
hand. These variables include the annual GDP growth rate per capita, which
provides a measure of the economic output per person. Data come from the
World Bank31. By incorporating this variable, we account for the economic
development of each country and its potential inuence on the relationship
being studied32. Furthermore, we include the size of the industrial sector as a
share of GDP in our analysis to account for potential changes in economic
structure that could affect both the policy measures taken and the emissions
prole. A decrease in a countrys industry share may suggest both lower
emissions and a reduced level of political protectionism towards the
respective economic branches32. In addition, we account for a selection of
political factors. Previous research has shown that democracies exhibit
stronger commitments to mitigate climate change and are more inclined to
cooperate in international treaties33,34. Here, we use a binary variable that
measures whether a country was a democracy in a respective year to account
for democratization processes that might affect our result. The variable
codes a country as a democracy if it fullls conditions for contestation and
participation35. In addition to these variables, we also account for climate
policies using the data from the Climate Policy Database when looking at
CO
2
emissions and vice versa, as both are likely to affect one another. By
including these control variables in our analysis, we aim to enhance the
robustness and accuracy of our ndings by considering important economic
as well as political factors that may have an impact on the relationship under
scrutiny.
We use an econometric technique that leverages variation in the timing
of the establishment of dedicated climate ministries. In our models, we use
the approach by Imai et al. which combines matching methods with a
difference-in-differences estimator17.Wecomparecountriesthathave
established a dedicated climate year in a respective year with those countries
that have a similar pre-treatment trajectory in terms of treatment history
(i.e., whether a country has had a previous climate ministry that had been
closed again) and time-variant covariates. This allows us to look at the
development of the effect of establishing a climate ministry over time.
Formally, the average treatment effect on the treated takes the following
form:
δF;LðÞ¼EYi;tþFXit ¼1;Xi;t1¼0;P
L
¼2
Xi;t

Xit
¼1;
Xi;t1¼0Yi;tþFXit ¼0;Xi;t1¼0;P
L
¼2
Xi;t

Xit
¼1;Xi;t1¼0
ð1Þ
Parameter Fenables us to estimate the cumulative treatment effect over
time. Due to the time coverage of our data, we set F=5.Thus,wemeasure
the treatment effect of establishing a climate ministry for up to 5 years after.
Furthermore, we adjust for treatment history up to 5 years before the
introduction of a ministry by setting L¼5. Country ithat establishes a
ministry in year t is the treated unit. Put differently, Xit ¼1aswellas
Xi;t1¼0. For these countries, Yi;tþFXit ¼1;Xi;t1¼0;PL
¼2Xi;t

is the potential outcome. Since we cannot observe the counterfactual out-
come had a country not introduced a climate ministry, we look at the
potential outcome of those countries that have not introduced a climate
ministry in a respective year, namely:
Yi;tþFXit ¼0;Xi;t1¼0;Xi;t

L
¼2

jXit ¼0;Xi;t1¼0ð2Þ
As the introduction of climate ministries is not randomly assigned, we
have to account for observed as well as unobserved confounders
(PK
k¼1ðXkit Þ). To account for time-invariant confounders, we use a
difference-in-differences estimator that solely looks at changes in the
dependent variable. Furthermore, we use Mahalanobis matching to ensure
that we only compare countries that are similar on a set of time-varying
confounders. The difference-in-differences estimator accounts for unob-
served time-invariant confounders under the condition that the parallel
trend assumption holds. Only comparing units during the same time per-
iods and additionally accounting for GDP growth trajectories via the
matching approach also ensure that our results are not driven by common
economic chocks such as the 2007 to 2008 nancial crisis.
Standard errors are computed by using the block-bootstrap procedure
introduced by Imai et al.17. In contrast to standard bootstrapping, this
procedure uses the weight each observation gets when matching and uses it
as a conditional factor instead of recomputing it in the bootstrapping
procedure.
https://doi.org/10.1038/s44168-024-00147-9 Article
npj Climate Action | (2024) 3:70 6
In addition to the difference-in-differences analysis, we also run a time-
series cross-sectional data analysiswithcarbonemissionspercapitain
metric tons as our dependent variable. Since we are interested in changes in
carbon emissions, we include country xedeffectsinourmodels.Weusea
stepwise approach to ensure that our results are not driven by covariate
choices. We start by solely including the existence of a climate ministry each
year plus country xed effects. Subsequently, we add year xed effects, our
control variables, and lagged levels of CO
2
emissions. We use standard OLS
standard errors.
Data availability
All data used in this article are available upon request.
Received: 18 December 2023; Accepted: 22 July 2024;
References
1. Hovi, J., Sprinz, DF., Sælen, H. & Underdal, A. The club approach: a
gateway to effective climate co-operation? Br. J. Polit. Sci. 49,
10711096 (2019).
2. Linsenmeier, M., Mohommad, A. & Schwerhoff, G. Global benets of
the international diffusion of carbon pricing policies. Nat. Clim.
Change 13, 679684 (2023).
3. Caballero, R. & Huber, M. State-dependent climate sensitivity in past
warm climates and its implications for future climate projections. Proc.
Natl. Acad. Sci. USA 110, 1416214167 (2013).
4. Dannenberg, A., Lumkowsky, M., Carlton, E. K. & Victor, D. G. Naming
and shaming as a strategy for enforcing the Paris Agreement: The role
of political institutions and public concern. Proc. Natl. Acad. Sci. USA
120, 2023 (2023).
5. Guy, J., Shears, E. & Meckling, J. National models of climate
governance among major emitters. Nat. Clim. Change 13,
189195 (2023).
6. Dubash, N. K. et al. National climate institutions complement targets
and policies. Science 374, 690693 (2021).
7. Mildenberger, M. The development of climate institutions in the United
States. Environ. Polit. 30,7192 (2021).
8. Tosun, J. Investigating ministry names for comparative policy
analysis: lessons from energy governance. J. Comp. Policy Anal. Res.
Pract. 20, 324335 (2018).
9. Schmidt, N. M. Late bloomer? Agricultural policy integration and
coordination patterns in climate policies. J. Eur. Public Policy 27,
893911 (2020).
10. Bauer, A., Feichtinger, J. & Steurer, R. The Governance of Climate
Change Adaptation in 10 OECD Countries: Challenges and
Approaches. J. Environ. Policy Plan. 14, 279304 (2012).
11. Boasson, E. L. National climate policy: a multi-eld approach
(Routledge, 2014).
12. von Lüpke, H., Leopold, L. & Tosun, J. Institutional coordination
arrangements as elements of policy design spaces: insights from
climate policy. Policy Sci. 56,4968 (2023).
13. Fernández-i-Marín, X., Knill, C. & Steinebach, Y. Studying policy
design quality in comparative perspective. Am. Political Sci. Rev. 115,
931947 (2021).
14. Wagner, P. M., Torney, D. & Ylä-Anttila, T. Governing a multilevel and
cross-sectoral climate policy implementation network. Environ. Policy
Gov. 31, 417431 (2021).
15. Fransen, T. et al. Taking stock of the implementation gap in climate
policy. Nat. Clim. Change 13, 752755 (2023).
16. Steinebach, Y. Instrument choice, implementation structures, and the
effectiveness of environmental policies: a cross-national analysis.
Regul. Gov. 16, 225242 (2022).
17. Imai, K., Kim, I. S. & Wang, E. H. Matching methods for causal
inference with time-series cross-sectional data. Am. J. Political Sci.
67, 587605 (2023).
18. Nascimento, L. et al. Twenty years of climate policy: G20 coverage
and gaps. Clim. Policy 22, 158174 (2022).
19. Henstra, D. Thetools of climate adaptationpolicy:analysinginstruments
and instrument selection. Clim. Policy 16, 496521 (2016).
20. Blanchard, O., Gollier, C. & Tirole, J. The portfolio of economic
policies needed to ght climate change. Annu. Rev. Econ. 15,
689722 (2023).
21. Schaffrin, A., Sewerin, S. & Seubert, S. Toward a comparative
measure of climate policy output. Policy Stud. J. 43, 257282 (2015).
22. Steinebach, Y. & Limberg, J. Implementing market mechanisms in the
Paris era: the importance of bureaucratic capacity building for
international climate policy. J. Eur. Public Policy 29,11531168 (2022).
23. Hanson, J. K. & Sigman, R. Leviathans latent dimensions: measuring
state capacity for comparative political research. J. Politics 83,
14951510 (2021).
24. Brambor, T., Clark, W. R. & Golder, M. Understanding interaction
models: improving empirical analyses. Political Anal. 14,6382 (2006).
25. Hainmueller, J., Mummolo, J. & Xu, Y. How much should we trust
estimates from multiplicative interaction models? Simple Tools to
improve empirical practice. Political Anal. 27, 163192 (2019).
26. Bayer, P. & Aklin, M. The European Union Emissions Trading System
reduced CO2 emissions despite low prices. Proc. Natl Acad. Sci. USA
117, 88048812 (2020).
27. Senninger, R., Finke, D. & Blom-Hansen, J. Coordination inside
government administrations: Lessons from the EU Commission.
Governance 34, 707726 (2021).
28. Nyrup, J. & Bramwell, S. Who governs? A new global dataset on
members of cabinets. Am. Political Sci. Rev. 114, 13661374 (2020).
29. Klüser, K. J. From bureaucratic capacity to legislation: how ministerial
resources shape governmentspolicy-making capabilities. West Eur.
Polit. 46, 347373 (2023).
30. Mortensen, P. B. & Green-Pedersen, C. Institutional effects of
changes in political attention: explaining organizational changes in the
top bureaucracy. J. Public Adm. Res. Theory 25, 165189 (2015).
31. World Bank World. Development Indicators (WDI) (The World
Bank, 2023).
32. Jahn, D. The politics of environmental performance (Cambridge
University Press, 2016).
33. Povitkina, M. The limits of democracy in tackling climate change.
Environ. Polit. 27, 411432 (2018).
34. Bättig, M. & Bernauer, T. National Institutions and Global Public
Goods: are democracies more cooperative in climate change policy?
Int. Organ. 63, 281308 (2009).
35. Boix, C., Miller, M. & Rosato, S. A complete data set of political
regimes, 18002007. Comp. Political Stud. 46, 15231554 (2013).
Acknowledgements
We would like to express our gratitude to the editors and anonymous
reviewers for their valuable suggestions on how to enhance our manuscript.
We also extend our thanksto the participantsof the Policy,Bureaucracy, and
Organization (PBO) workshop in Geilo, members of the Environmental
Politics and Governance (EPG) Group (online), and attendees of the
Research Colloquium at the Chair of Christoph Knill at the LMU Munich for
their feedback. This research was funded by the Norwegian Research
Council (ACCELZ Project, Grant No. 335073) and received Småforsk
funding from the Department of Political Science at the University of Oslo.
Author contributions
J.L., Y.S. and J.N. have made substantial contributions to the conception or
design of the work or the acquisition, analysis, or interpretation of the data;
drafted the work or revised it critically for important intellectual content;
approved the completed version, and are accountable for all aspects of the
work in ensuring that questionsrelated to the accuracyor integrity of any part
of the work are appropriately investigated and resolved. J.L., Y.S. and J.N.
have read and approved the nal manuscript.
https://doi.org/10.1038/s44168-024-00147-9 Article
npj Climate Action | (2024) 3:70 7
Competing interests
The author declares no competing interests.
Additional information
Supplementary information The online version contains
supplementary material available at
https://doi.org/10.1038/s44168-024-00147-9.
Correspondence and requests for materials should be addressed to
Yves Steinebach.
Reprints and permissions information is available at
http://www.nature.com/reprints
Publishers note Springer Nature remains neutral with regard to
jurisdictional claims in published maps and institutional afliations.
Open Access This article is licensed under a Creative Commons
Attribution 4.0 International License, which permits use, sharing,
adaptation, distribution and reproduction in any medium or format, as long
as you give appropriate credit to the original author(s) and the source,
provide a link to the Creative Commons licence, and indicate if changes
were made. The images or other third party material in this article are
included in the articles Creative Commons licence, unless indicated
otherwise in a credit line to the material. If material is not included in the
articles Creative Commons licence and your intended use is not permitted
by statutory regulation or exceeds the permitted use, you will need to
obtain permission directly from the copyright holder. To view a copy of this
licence, visit http://creativecommons.org/licenses/by/4.0/.
© The Author(s) 2024
https://doi.org/10.1038/s44168-024-00147-9 Article
npj Climate Action | (2024) 3:70 8
ResearchGate has not been able to resolve any citations for this publication.
Article
Full-text available
Carbon pricing policies are essential for mitigating climate change, but the global benefits of leadership and the international diffusion of these policies are not well understood. Here we provide robust and statistically significant evidence showing that the adoption of carbon pricing in one country can explain the subsequent adoption of carbon pricing in other countries. For a neighbouring country, diffusion increases the probability of policy adoption on average by several percentage points. Translating these empirical estimates with Monte Carlo simulations into global reductions in emissions through policy diffusion suggests that for many countries, decreases in emissions as a result of diffusion could be larger than domestic emission reductions. These results support the adoption of stringent climate policies, especially in countries in which climate change mitigation might be considered as not very important because of relatively low levels of domestic emissions.
Article
Full-text available
National climate institutions structure the process of climate mitigation policymaking and shape climate policy ambition and performance. Countries have, for example, been building science bodies, passing climate laws and creating new agencies. Here we provide the first systematic comparison of climate institutions across 21 of the largest emitters. Drawing on an original dataset, we identify in a bottom-up cluster analysis four national models of climate governance: Climate Technocracies, Climate Developmentalists, Carbon Fragmentists and Carbon Centralists. These national models of climate governance are associated with policy ambition and performance. Climate Technocracies and Developmentalists tend to score higher than Carbon Fragmentists and Centralists in policy ambition and performance. The relative ambition of national models of governance is associated with some macro-institutional and macro-economic features, but not others. This suggests potential for domestic and international policymakers to invest in building national climate institutions across country settings to strengthen climate policy capacity. National climate institutions could greatly impact the process of policy design and implementation. This analysis identifies four models of climate governance for major emitters, estimates their policy ambitions and performance, then shows how they are related to macro features.
Article
Full-text available
This study offers insights into the institutional arrangements established to coordinate policies aiming at the mitigation of and adaptation to climate change. Drawing on the literature on policy design, we highlight institutional arrangements as elements of policy design spaces and contend that they fall into four categories that either stress the political or problem orientation of this activity: optimal, technical, political, and sub-optimal. We use original data on 44 major economies and greenhouse gas-emitting countries to test this expectation. These data capture various properties of national coordination arrangements, including the types of coordination instruments in place, the degree of hierarchy, the lead government agency responsible for coordination, and the scope of cross-sectoral policy coordination. The dataset also captures the degree to which non-state actors are involved in coordination and whether coordination processes are supported by scientific knowledge. Using cluster analysis, we show that the institutional arrangements for the horizontal coordination of climate policy do indeed fall into the four above-mentioned categories. The cluster analysis further reveals that a fifth, hybrid category exists. Interestingly, the political orientation dominates in the institutional arrangements for the horizontal coordination of climate change mitigation, whereas the problem orientation is more important in the arrangements for the horizontal coordination of climate change adaptation.
Article
Full-text available
How does ministries’ capacity to draft legislation affect the political output of modern governments? This article combines a novel dataset describing the capacity of ministerial bureaucracies to attend to about 250 distinct policy issues with content-coded data on government legislation. The sample consists of Danish, Dutch and German governments, jointly spanning the time from 1995 to 2013. The analysis reveals three main findings: firstly, issue-specific bureaucratic capacity unconditionally increases governments’ legislative activity; secondly, legislative activity is stifled if bureaucratic capacity is spread across different ministries; thirdly, against theoretical expectations the productive effect of bureaucratic capacity is not positively related to governments’ issue salience. The results indicate that the design and resources of ministerial portfolios affect policy making in western governments.
Article
Full-text available
The number and coverage of climate change mitigation policies have increased in the past twenty years, but important policy adoption gaps remain. To analyse sectoral climate policy in the G20 over time (2000–2019), we compiled a dataset of climate change mitigation-relevant policies and identified 50 key policy options that constitute a comprehensive sectoral climate policy package. Approximately half of these policy options are not widely adopted. Adoption is particularly low for policies that aim to: phase out coal and oil and mandate energy reductions in electricity and heat supply; reduce industrial process emissions and incentivise fuel switch in industry; design urban planning strategies for retrofits; and support the use of renewable energy for cooking and heating/cooling purposes in buildings. Policies to remove fossil fuel subsidies and support carbon dioxide removal also need substantial improvement. However, many policy adoption gaps exist as the coverage of at least one policy option could be improved in each sector. Policy adoption gaps leave at least one-tenth of the G20’s emissions completely uncovered. Filling these gaps is fundamental to realize the full mitigation potential of existing policy options and to advance the transition towards global net zero greenhouse gas emissions. Key policy insights • Mitigation-related policy options can be presented as a matrix by sector to shed light on what constitutes a comprehensive climate policy package; looking across sectoral climate policies helps to unpack and clarify the status of adoption. • Policy adoption gaps exist in all sectors. Increasing the sectoral coverage of climate policies will help to ensure that all relevant sectoral emissions and mitigation areas are considered in national mitigation efforts. • Even if an increase in policy coverage alone does not ensure emission reductions, the absence of policy coverage indicates that emissions can still be further reduced and that a portion of global emissions remain uncovered by policies. • Despite the observed increase in the number and coverage of climate policies, slow progress towards reducing global emissions and meeting the collective Paris climate goals calls for more comprehensive climate change mitigation policies. Filling policy adoption gaps presents a concrete strategy to improve sectoral, national and global climate policy.
Article
Enforcement is a challenge for effective international cooperation. In human rights and environmental law, along with many other domains of international cooperation, "naming and shaming" is often used as an enforcement mechanism in the absence of stronger alternatives. Naming and shaming hinges on the ability to identify countries whose efforts are inadequate and effectively shame them toward better behavior. Research on this approach has struggled to identify factors that explain when it influences state behavior in ways that lead to more cooperation. Via survey of a large (N = 910) novel sample of experienced diplomats involved in the design of the Paris Agreement, we find support for the proposition that naming and shaming is most accepted and effective in influencing the behavior of countries that have high-quality political institutions, strong internal concern about climate change, and ambitious and credible international climate commitments. Naming and shaming appears less effective in other countries, so further enforcement mechanisms will be needed for truly global cooperation. We also find that the climate diplomacy experts favor a process of naming and shaming that relies on official intergovernmental actors, in contrast with studies suggesting that NGOs, media, and other private actors are more effective at naming and shaming. We suggest that these tensions-the inability for naming and shaming to work effectively within the countries least motivated for climate action and the preference for namers and shamers that seem least likely to be effective-will become central policy debates around making cooperation on climate change more enforceable.
Article
Climate change poses an existential threat. Theoretical and empirical research suggest that carbon pricing and green R&D support are the right tools, but their implementation can be improved. Other policies, such as standards, bans, and targeted subsidies, also all have a role to play, but they have often been incoherent, and their implementation is delicate. Expected final online publication date for the Annual Review of Economics, Volume 15 is August 2023. Please see http://www.annualreviews.org/page/journal/pubdates for revised estimates.
Article
Matching methods improve the validity of causal inference by reducing model dependence and offering intuitive diagnostics. Although they have become a part of the standard tool kit across disciplines, matching methods are rarely used when analysing time‐series cross‐sectional data. We fill this methodological gap. In the proposed approach, we first match each treated observation with control observations from other units in the same time period that have an identical treatment history up to the prespecified number of lags. We use standard matching and weighting methods to further refine this matched set so that the treated and matched control observations have similar covariate values. Assessing the quality of matches is done by examining covariate balance. Finally, we estimate both short‐term and long‐term average treatment effects using the difference‐in‐differences estimator, accounting for a time trend. We illustrate the proposed methodology through simulation and empirical studies. An open‐source software package is available for implementing the proposed methods.