- 1Centre for Climate Change and Social Transformations (CAST), School of Psychology, Cardiff University, Cardiff, Wales, United Kingdom
- 2Welsh School of Architecture, Cardiff University, Cardiff, Wales, United Kingdom
- 3Centre for Climate Change and Social Transformations (CAST), Department of Psychology, University of Bath, Bath, United Kingdom
- 4School of Psychology, Swansea University, Swansea, Wales, United Kingdom
- 5Ipsos UK, London, United Kingdom
Achieving ambitious carbon reduction targets requires transformative change to society, with behaviour change playing an important role. Climate change mitigation (‘net zero’) policies are needed to accelerate and support such behaviour change. This study examined factors and framing effects in public support for net zero policies in the United Kingdom (UK), making use of a large probability sample (ntotal = 5,665) survey conducted in August 2021. It found that net zero policies are widely supported, with only taxes on red meat and dairy products being supported by less than half of the UK public. Climate worry and perceived fairness were the strongest and most consistent predictors of policy support for net zero policies. The results further suggest that support for net zero policies can be increased by emphasising the co-benefits of the policies, in particular where they are beneficial for health. However, the framing effects were very small. In contrast, public support for net zero policies is lower when potential lifestyle and financial costs are mentioned. This suggests that perceived fairness of the distribution of costs and lifestyle implications of policies are crucial for building and maintaining support for net zero.
Introduction
Background
Climate change poses profound risks to humans, animals and ecosystems, ranging from rising sea levels and extreme weather to spread of disease and crop failures (IPCC, 2021). In order to mitigate these risks, and limit global warming to no more than 2°C above pre-industrial levels, carbon emissions from human activities need to be substantially reduced and reach ‘net zero’ by 2050 (IPCC, 2022). Net zero means reducing all possible carbon emissions and then offsetting any remaining emissions (Fankhauser et al., 2022). The United Kingdom (UK) was the first country to implement legally-binding targets to reduce carbon emissions, with a target of reaching net zero by 2050 and 78% reduction in emissions by 2035 (UK Government, 2008, 2019). This will however require transformative change, with behaviour change playing a central role in that transformation. Most of the measures needed to reach net zero require at least some behavioural change, including the adoption of low-carbon technologies and wider lifestyle changes (Carmichael, 2019; Climate Change Committee, 2020; IPCC, 2022).
Public concern about climate change has been rising gradually over the past 10 years, and now large majorities in most countries say they are worried about climate change (Poortinga et al., 2019; Ipsos, 2023). In addition, people recognise the urgency with which climate change needs to be addressed and are also aware of the need for change (Steentjes et al., 2021). However, environmental action remains largely limited to small-scale lifestyle changes, such as recycling (Whitmarsh, 2009; Ipsos, 2023). More impactful actions are needed to substantially reduce greenhouse gas emissions, including avoiding flying and driving and adopting plant-based diets (Wynes and Nicholas, 2017; Ivanova et al., 2020). Many of these impactful actions do not only reduce greenhouse gas emissions, but also provide benefits for health, the economy and the environment. A move towards more plant-based diets not only has the potential to reduce food-related greenhouse gas emissions by up to 70 percent, it also can help to reduce global mortality by up to 10 % (Springmann et al., 2016). There are also clear health benefits associated with a shift to lower-carbon transport modes. A shift to electric vehicles, public transport and active travel modes reduces congestion, air and noise pollution, and road accidents (Smith et al., 2016), with additional health benefits of increased exercise from walking and cycling (Shaw et al., 2014).
While these behavioural changes can help achieve wider sustainability goals and improve human wellbeing (Creutzig et al., 2022), they can be costly; and many individuals report substantial barriers (e.g., costs, inconvenience, etc.) to environmental action. For example, switching to a more plant-based diet provides health benefits, but may also involve paying more for ingredients or learning new food preparation skills (Whitmarsh et al., 2021). Meaningful policies are therefore needed to enable the behaviour change required to reach net zero. Regulation, economic (dis)incentives, and changes to infrastructure can all be used to promote low-carbon and discourage high-carbon options (Grubb et al., 2020; House of Lords, 2022). Yet, these policies are often controversial and have sparked high profile protests in some cases (Howarth et al., 2020). Indeed, several policies to enable low-carbon behaviour to have met with considerable public opposition. Low Traffic Neighbourhoods (LTN) that use modal-filters to restrict through traffic in residential areas have proven to be controversial (Aldred, 2019; Campbell, 2023), as has the implementation of new cycle lanes as part of the Emergency Active Travel Fund that was designed to promote walking and cycling in response to the COVID-19 pandemic (Morton, 2020; Campbell, 2023). Similarly, policies to reduce red and processed meat consumption lack widespread support (Pechey et al., 2022), not least because there are perceived as being not particularly effective (Steentjes et al., 2021). Furthermore, meat consumption remains deeply embedded in social and cultural norms (Sievert et al., 2022), and meat curtailment policies are often seen as an infringement on freedom of choice (Michielsen and van der Horst, 2022).
Understanding the basis of public support for and opposition to net zero policies is essential for their effective design and implementation. Previous research demonstrates that public participation in environmental policy design can improve its efficacy and acceptability, since engaging with diverse groups can shed light on the workability and perceived fairness of policies and increase trust in and legitimacy of the policy process (Stern and Dietz, 2008; Höppner and Whitmarsh, 2012). With regards to climate change policies, given the scale of disruption these may bring to lifestyles and the economy, it is essential to foster public buy-in for these changes but also to understand why different policies may be accepted or rejected and how support may be fostered. Understanding public support for net zero policies can also create the political mandate needed for ambitious climate policies, emboldening leaders to act in line with voter preferences (Howarth et al., 2020).
Factors in support for net zero policies
The literature suggests that people are more likely to support environmental policies if they are seen as effective in addressing the problem at hand (e.g., reducing air pollution, congestion etc) and/or provide clear benefits for society as a whole or for oneself personally (Dieplinger and Fürst, 2014; Schwirplies et al., 2019; Schuitema et al., 2020). At the same time, non-coercive ‘pull’ measures, such as subsidies, financial support and information provision are supported more than coercive ‘push’ policies, such as regulation and taxes (Eriksson et al., 2008; Drews and van den Bergh, 2016). In particular, information provision, which fully maintains individual choice and generally does not impose costs on the individual, is seen as inoffensive and therefore supported across the board (Poortinga et al., 2022). Perceptions of coerciveness, however, depend on people’s personal circumstances. People are less likely to support a policy if they think they will be personally affected it. For example, in particular car owners perceive road pricing as an infringement on freedom, and therefore are more likely to oppose such measures (Jakobsson et al., 2000; Fujii et al., 2004; Hammar and Jagers, 2007).
Another key factor in policy acceptance is perceived fairness. People are more likely to support climate policies if they think they are fair. Indeed, perceived fairness is often a stronger predictor of climate change policy support than perceived effectiveness (Ejelöv and Nilsson, 2020; Bergquist et al., 2022). Perceived fairness has distributive and procedural components. Perceived distributive fairness involves perceptions of how costs and rewards of a policy are shared across different groups, while perceived procedural fairness refers to the fairness of processes by which decisions are made, in particular whether the decision-making process is transparent and takes into account views of everyone affected (Greenberg, 1986). The acceptance of and support for environmental policies are dependent on both perceived distributive fairness and perceived procedural fairness (Besley, 2010; Schmöcker et al., 2012; Dreyer and Walker, 2013; Kim et al., 2013; Liu et al., 2020). People are more likely to support policies that target those who are the most responsible and do not disproportionately affect vulnerable or (economically) disadvantaged groups. That is, people are more supportive of policies that are proportional to current and historical emissions, i.e., adopt a ‘polluter pays’ principle, and take account of someone’s ‘ability to pay’ (Cai et al., 2010; Bechtel and Scheve, 2013), as well as polices that have consulted all groups that are likely to be affected and are considerate of them (Climate Assembly UK, 2020). The extent to which policies are seen as fair and thus supported does however vary across different socio-demographic groups, such as income, age and place of residence (Player et al., 2023). This may be due to different needs, opportunities and abilities, which is likely to impact upon the extent the different groups are affected by the policy (Player et al., 2023).
Individual values and attitudes are important factors in policy support (Bouman et al., 2020). Problem perception has been identified as a key determinant of policy support in theories such as the Value-Belief-Norm model of pro-environmental behaviour (Stern, 2000). Consequently, climate change concern is a strong driver of climate policy acceptance (Bergquist et al., 2022). Furthermore, environmental values are linked to lower opposition to ‘push’ policies, like congestion charging (Eliasson and Jonsson, 2011) and carbon taxes (Eriksson et al., 2008), and political orientation predicts climate policy support in many countries (Poortinga et al., 2019). In the US, for example, right-wing orientation is associated with lower support for publicly-financed climate policies (Ziegler, 2017).
Taken together, evidence shows both personal factors (e.g., socio-demographics, climate worry, political values) and policy-specific evaluations (e.g., perceived fairness) shape policy acceptance. However, while studies have examined predictors of specific climate policies or class of policy (e.g., carbon taxation), little work has compared the predictors of a diverse range of net zero measures that span sectors (transport, food, finance, etc.) and instrument type (e.g., regulation, taxation). This limits the comparability and utility of studies, and is an important evidence gap we address in the current study.
Framing effects in support for net zero policies
While support for climate policies may vary between different groups, research shows that the way in which policies are communicated or ‘framed’ can also shape support. Framing is how an issue or action is presented, emphasising certain aspects of an issue, often with the intention to influence how an audience perceives it (Lockwood, 2011). In some instances, communicating a policy’s co-benefits, for example for health or finances, may boost policy acceptability. Positively framed health messages can make climate change appear local, short-term, and personal, increasing policy acceptability (Rossa-Roccor et al., 2021). Co-benefits, such as safety, health, or job creation, have also previously increased policy support (Jennings et al., 2020; Dechezleprêtre et al., 2022), and participatory methods such as the UK Climate Assembly UK (2020) have been cited as opportunities to explore policy co-benefits that the public otherwise may not consider. Since people’s preferences for co-benefits vary in line with their personal values, tailoring co-benefit framing to the specific populations may boost acceptability (Whitmarsh and Corner, 2017). Overall, however, framing effects on policy support tend to be small (Bernauer and McGrath, 2016), with some arguing that citizens are overexposed to competing climate-related ‘frames’ in their everyday lives, making experimentally manipulated framing effects challenging to detect and unreliable (Fesenfeld and Rinscheid, 2021). Nevertheless, framing studies shed light on how policies that are designed to achieve climate goals can be communicated in ways that focus on other societal goals and thus achieve wider public support beyond committed green voters. This is arguably a critical goal for achieving political and public consensus on the transition to net zero (Giddens, 2009).
Aims of the study
This study explores factors and framing effects in public support for climate change mitigation (‘net zero’) policies in the UK. First, the study examines the extent to which eight net zero policies are opposed or supported by the UK public. Second, it assesses the impacts of benefit framing (in terms of climate change, health and economic benefits) on public support for the net zero policies. Third, it examines how personal and policy-specific factors shape policy support for net zero policies. In particular, it examines how socio-demographic factors, climate worry and political values, as well as perceived fairness of the net zero policies, are associated with policy support. Finally, the study explores the impact that potential personal costs (e.g., having to make lifestyle changes, taking on financial costs) may have on support for net zero. This is to examine whether support for net zero policies is conditional on the potential lifestyle or financial implications they may have.
Methods
The net zero living study
The Ipsos-CAST net zero living study was conducted between 19 and 25 August 2021, using the Ipsos UK Knowledge Panel (Ipsos & CAST, 2022). The Ipsos UK Knowledge Panel is an online random probability panel consisting of members of the UK public who have been recruited using address-based random probability sampling. Data were weighted for age, gender, region, deprivation quintile, education, ethnicity, and number of adults in the household to make the sample fully reflective of the UK population. In total, 5,665 people aged 16 years or older took part in the survey. The characteristics of the sample are described in Table 1.
The study focused on eight net zero policies covering the areas of diet, transport, material consumption, home heating and green finance policy, which are all areas where individual level action is needed to reach net zero. It used policies that already exist or are being discussed in the UK, so that survey respondents could easily envisage the policies and thus have or form an opinion about them (Ipsos & CAST, 2022). The study included policies such as subsidies for electric vehicles, which already exist in the UK (UK Government, 2023) and low traffic neighbourhoods (LTNs) that have received widespread media attention (Dudley et al., 2022). Other proposed policies were selected from existing reports, such as the frequent flyer levy discussed at the Climate Assembly UK (2020).
Procedure
Respondents were presented descriptions of four out of eight policies and asked several questions about these policies, including their level of support and their views on the fairness of the policies (each policy was assessed by n = 2,731–2,887 respondents). The policies were randomly allocated to each respondent. In order to examine the impact of different framings on support for net zero policies, respondents were also randomly presented one of four descriptions of the net zero policies: (1) a ‘neutral’ description, which contained a technical description of the policies as shown in Table 2, (2) a ‘climate change’ framing, presenting the potential climate impact of the policy, (3) a ‘health’ framing, presenting the potential health, safety or general lifestyle impacts of the policy, or (4) an ‘economic’ framing, presenting the potential financial impacts of the policy. All versions contained the neutral description of the policies with added text for the other framings (See Supplementary Information Table SI1).
Table 2. Descriptions of the net zero policy (see also Ipsos & CAST, 2022).
Measures
Dependent variables
The main dependent variable in this study was support for net zero policies. This was measured with a single item (“To what extent do you support or oppose this?”), with a 5-point response scale (1 “Strongly oppose,” 2” Tend to oppose,” 3 “Neither support nor oppose,” 4 “Tend to support,” and 5 “Strongly support”). The included net zero policies were: creating low traffic neighbourhoods (LTN), frequent flyer levies, electric vehicle (EV) subsidies, phasing out the sale of gas and coal boilers, changing product pricing to reflect how environmentally friendly products are, ensuring access to sustainable pension funds, increasing vegetarian/vegan options in public food provisioning, and higher taxes on red meat and dairy products. A description of the policies is provided in Table 2.
Two additional dependent variables were used to measure the level of conditional support for net zero policies if they would have potential lifestyle or potential financial implications, respectively. The questions were phrased as “If this policy meant that …, to what extent would you support or oppose it?.” The same response scale was used as for the main support for net zero policies variable. The phrasing of the questions for each of the eight net zero policies is shown in the Supplementary Information Table SI2.
Independent variables
The independent variables in this study included personal and policy-specific factors. The personal factors included socio-demographics (gender, age, ethnic background, country, type of area, deprivation), climate change worry, and political values (left vs. right wing orientation, liberal vs. authoritarian). The policy-specific variable included here was perceived fairness of the net zero policies (see below). A framing variable used dummies to indicate how net zero policies were presented to the respondents (i.e., the ‘neutral’ control text or a climate change, health or economic framing). This was done to control for any faming effects in the regression analyses.
Gender included the male and female categories; age was subdivided into three groups of 16–34 years, 35–54 years, and 55 years and older; ethnic background was subdivided into White (including white minority groups) and other ethnic backgrounds (which included Asian/Asian British. Black/Black British, and mixed, multiple, and other ethnic groups); country covered the four home nations (England, Scotland, Wales and Northern Ireland), with a separate English sub-category for London; and area type indicated whether respondents lived in a rural or urban area. All these socio-demographic groups were included as dummy variables. Deprivation reflected the Index of Multiple Deprivation (IMD) quintile. The latter variable was included as a continuous variable.
Climate change worry was measured by asking respondents “How worried are you about climate change?.” The response scale ranged from 1 (not at all worried) to 5 (extremely worried). The worry scale was adapted from (Poortinga et al., 2019). To explore the role of political values we adopted and measured two political values dimensions, i.e., a ‘left versus right’ and a ‘liberal versus authoritarian’ dimension. These constructs were measured using twelve attitude-style statements developed by Evans and colleagues (Evans et al., 1996), with six statements measuring the ‘left versus right’ dimension (“Ordinary working people get their fair share of the nation’s wealth,” “There is one law for the rich and one for the poor,” “There is no need for strong trade unions to protect employees’ working conditions and wages,” “Private enterprise is the best way to solve Britain’s economic problems,” “Major public services and industries ought to be in state ownership,” “It is the government’s responsibility to provide a job for everyone who wants one”) and six statements measuring the ‘liberal versus authoritarian’ dimension (“Young people today do not have enough respect for traditional British values” “Censorship of films and magazines is necessary to uphold moral standards,” “People should be allowed to organise public meetings to protest against the government,” “People in Britain should be more tolerant of those who lead unconventional lives,” “For some crimes, the death penalty is the most appropriate sentence, “People who break the law should be given stiffer sentences”). Respondents could use a 5-point scale ranging from 1 “strongly disagree” to 5 “strongly agree.” The two scales showed good internal consistency (Cronbach’s α of 0.73 and 0.74, respectively) and were only moderately inter-correlated (r = 0.36). The ‘left–right’ and ‘libertarian-authoritarian’ dimensions were standardised by transforming them into Z-scores.
Perceived fairness of net zero policies was measured with three items. Respondents were asked “How confident, if at all, are you that this policy would…” (a) give a fair outcome to everyone affected, (b) take into account the views of everyone affected, and (c) not be biased towards any one particular group. Respondents could respond using a 4-point scale ranging from 1 “Not at all confident” to 4 “Very confident.” The items were averaged and formed coherent scales for all eight policies (Cronbach’s α’s ranged between 0.84 and 0.88).
Statistical analyses
First, descriptive analyses were used to show the extent to which the eight net zero policies were supported or opposed. Second, univariate (one-way) Analyses of Variance (ANOVAs) were conducted to examine whether the different framings have an impact on public support for the eight net zero policies. Where an overall ANOVA was significant, a Tukey’s HSD Test was conducted to see which framings were significantly different from the control group. Eta squared (η2) are reported for the effect sizes. Third, linear regression and multilevel modelling were used to examine factors in public support for the different net zero policies. Separate linear regressions were conducted for each policy, with policy support as the dependent variable. Multilevel modelling was used to examine factors in support across the eight net zero policies. In the multilevel analysis, support for the eight policies were seen as repeated measures (Level 1) within individuals (Level 2). This multilevel approach allows consistent effects of the factors to be estimated across the eight net zero policies. Independent variables included socio-demographics, climate change worry and political values variables, and perceived fairness of the policies. Finally, T-tests were conducted to test whether mentioning potential lifestyle and financial implications changes support for the net zero policies. Cohen’s d are reported for the effect sizes. All statistical analyses were conducted in RStudio v2021.09.0, with a number of R packages, including tidyverse (Wickham et al., 2019), psych (Revelle, 2022), and lme4 (Bates et al., 2015).
Results
Support for net zero policies
Figure 1 shows that there is widespread public support for the net zero policies that were included in the study, with low levels of opposition (also see Ipsos & CAST, 2022). Comfortable majorities support seven of eight policies presented. The highest levels of support were found for frequent flyer levies (68%), followed by changing product pricing to reflect how environmentally friendly products are, phasing out the sale of gas and coal boilers and electric vehicle subsidies (each 62%). Ensuring access to sustainable pension funds were supported by 55%. The results suggest that there is higher support for transport, energy and consumption-related policies than for food and diet-related policies, but further research with a wider range of polices is needed to solidify such a claim. The lowest levels of support in this study were for higher taxes on red meat and dairy products. Less than half of the population supported this policy. It is relevant to note that support (47%) was still higher than opposition (32%).
Framing effects in support for net zero policies
Table 3 shows the mean support ratings and standard deviations for the different benefit framing of the eight net zero policies (also see Figure 2). The framing effects for EV subsidies [F(3, 278) = 14.500, p = 0.000, η2 = 0.015], environmental pricing [F(3, 2,767) = 11.040, p = 0.000, η2 = 0.012], and sustainable pensions [F(3, 2,673) = 3.928, p = 0.008, η2 = 0.004] were significant. Inspection of mean support ratings and the results of Tukey’s HSD post-hoc tests shows that all framings increased support for EV subsidies; that the health and economic (but not climate change) framings increased support for environmental pricing; and that only the health framing increased support for sustainable pensions. The framing effects for the other policies were non-significant [LTN: F(3, 2,784) = 1.528, p = 0.205, η2 = 0.002; Frequent flyer levy: F(3, 2,782) = 0.194, p = 0.901, η2 = 0.000; Vegan options: F(3, 2,792) = 1.163, p = 0.322, η2 = 0.001; Meat taxes: F(3, 2,773) = 0.850, p = 0.466, η2 = 0.001; Phasing out boilers: F(3, 2,775) = 1.597, p = 0.188, η2 = 0.002].
Table 3. Mean support (M) and standard deviations (SD) for different benefit framings of net zero policies.
Factors in support for net zero policies
Table 4 presents the results of the linear regression analyses for policy support. It shows that women express higher levels of support for increasing vegan options in public food provisioning and environmental pricing. It further shows that older age groups (and in particular those aged 55 and over) express higher levels of support for LTNs, frequent flyer levies, meat taxes, environmental pricing and phasing out boilers. Respondents with a non-white ethnic background express lower levels of support for LTNs, frequent flyer levies and environmental pricing.
Table 4 also shows that support for the net zero polices vary across different geographical areas. Respondents living in Scotland express less support for increasing vegan options in public food provisioning, meat taxes and environmental pricing; respondents living in Wales express less support for increasing vegan options in public food provisioning; and respondents living in London shows less support for LTNs as compared to those living in England (outside of London). Respondents from urban areas express lower levels of support for frequent flyer levies than those from rural areas, while respondents from more deprived neighbourhoods express lower levels of support for EV subsidies, increasing vegan options in public food provisioning and environmental pricing than those from less deprived areas.
In terms of the psychological variables, climate change worry is the most consistent personal factor in support for the net zero policies: those with higher levels of worry about climate change have higher levels of support for all net zero policies. In terms of political values, more right-wing individuals have lower levels of support than more left-wing individuals for all net zero policies except environmental pricing, while respondents with more authoritarian views express less support for net zero policies than those with more liberal views. The strongest effects were found for perceived fairness. That is, those who perceive a net zero policy to be fair express higher levels of support for them, as compared to those who do not perceive a policy to be fair.
The regression analyses also included the framing variable indicating how the net zero policies were presented to the respondents, showing whether there is a framing effect when all personal and policy-specific factors are controlled for. The results depart slightly from the univariate analysis of variance reported above, in that no significant effects were found for meat taxes and for sustainable pensions. Conversely, and also in contrast to the univariate ANOVA results, the health framing was found to increase support for phasing out gas/coal boilers. Largely in line with the univariate ANOVA results, all framing conditions (i.e., climate change, health, and economic) were found to increase support for EV subsidies and for environmental pricing.
The final column of Table 4 presents the results of the multilevel model with policy support ratings (Level 1) nested within individuals (Level 2). The results suggest that women and older age groups have higher levels of support for net zero policies overall. Respondents from Scotland and Wales express slightly lower level of support for net zero policies than those from England. In line with the individual regression analyses, respondents with higher levels of worry about climate change express more support across the eight net zero policies; respondents with more right-wing and authoritarian views express less support for net zero policies; and perceived fairness was the strongest predictor of support across the eight net zero policies. The results further suggest that a health framing may increase support across the eight net zero policies.
Support for net zero policies with potential lifestyle and financial implications
Table 5 shows mean support for the eight net zero policies with and without mentioning potential lifestyle and financial implications. It is clear that mean support for the net zero policies is lower when potential personal implications of these policies are mentioned. The only exception is Environmental pricing, for which support is higher when potential lifestyle implications are mentioned, t(2718) = −15.87, p < 0.001 (Cohen’s d = 0.28). For all other cases support decreased when mentioning potential lifestyle implications (Frequent flyer levy, t(2394) = 32.239, p < 0.001, Cohen’s d = 0.56; Sustainable pensions, t(2308) = 22.289, p < 0.001, Cohen’s d = 0.50; EV subsidies, t(2599) = 18.769, p < 0.001, Cohen’s d = 0.30; Phasing out boilers, t(2573) = 24.434, p < 0.001, Cohen’s d = 0.35; Vegan options, t(2690) = 23.553, p < 0.001, Cohen’s d = 0.30; LTN, t(2612) = 21.106, p < 0.001, Cohen’s d = 0.32; and Meat taxes, t(2674) = 13.481, p < 0.001, Cohen’s d = 0.20). Mentioning potential financial implications decreased support for all eight net zero policies [Frequent flyer levy, t(2433) = 36.942, p < 0.001, Cohen’s d = 0.68; Environmental pricing, t(2738) = 12.450, p < 0.001, Cohen’s d = 0.20; Sustainable pensions, t(2450) = 55.437, p < 0.001, Cohen’s d = 1.21; EV subsidies, t(2591) = 33.450, p < 0.001, Cohen’s d = 0.56; Phasing out boilers, t(2573) = 39.257, p < 0.001, Cohen’s d = 0.64; Vegan options, t(2715) = 42.943, p < 0.001, Cohen’s d = 0.70; LTN, t(2710) = 47.340, p < 0.001, Cohen’s d = 0.86; and Meat taxes, t(2675) = 17.860, p < 0.001, Cohen’s d = 0.27].
Table 5. Mean support (M) and standard deviations (SD) for net zero policies with and without potential lifestyle and financial implications.
Discussion
Summary of results
Meeting ambitious carbon reduction targets to keep climate change within safe limits requires transformative change to society. The transformation to net zero needs to be accelerated by public policy to ensure the reductions are made in time (Roberts et al., 2018). This needs to involve policies that support behaviour change across a range of activities and domains to reduce carbon emissions (Nielsen et al., 2020), as technological change alone is not sufficient (Akenji et al., 2021).
This study provides new insights into public support for net zero policies in the UK, by exploring factors and framing effects across a range of net zero policies. In particular, it considered personal and policy-specific factors in support for eight policies that are already enacted or considered in the UK in a number of behavioural domains, and examined whether framing net zero policies in terms of their benefits can help to increase public support for them. Furthermore, the study explored whether mentioning potential cost and lifestyle implications of net zero policies can affect support for them.
The study found more support than opposition for all eight net zero policies. The highest levels of support were found for frequent flyer levies, environmental product pricing, phasing out the sale of gas and coal boilers, and electric vehicle subsidies. The lowest levels of support were found for taxes on meat and dairy products. This was the only policy with less than 50% support among the UK public. Relatively low levels of support were also found for LTNs and increasing vegetarian and vegan options in public food provisioning.
These results are in line with other research in the UK and elsewhere showing that the public understand the importance of policies targeting transport, energy and material consumption behaviours (Steentjes et al., 2021). However, they tend to underestimate carbon emissions from food (Wynes et al., 2020) and often do not see the necessity for change in this area (Steentjes et al., 2021). This may at least partly explain why there is lower support for higher taxes on red meat and dairy products, although the label ‘tax’ is also known to decrease support compared to equivalent concepts, such as ‘levy’ (Baranzini and Carattini, 2017). A repeat of the survey conducted in Autumn 2022 shows that support for the net zero policies has remained high despite the cost-of living-crisis. Some policies even enjoyed higher support in 2022 than in 2021 (see Supplementary Information Table SI3).
The study further demonstrated that framing net zero policies in terms of their co-benefits can improve public support, but the effects are quite small. The health framing was particularly effective in increasing public support for net zero policies, with some effects found for the economic and climate change framings as well. It should be noted that the co-benefit frames did not increase support for four out of eight policies (i.e., frequent flyer levies, phasing out boilers, increasing vegetarian/vegan options, and LTNs). It may be that some of these policies are already associated with specific co-benefits, which might explain why the different framings were not very successful in increasing support. The current evidence on the effects of co-benefits framing is mixed. While some research has found consistent effects across a large number of countries (Bain et al., 2016), others conclude that an alternative framing or justification for climate policy is unable to increase public support for climate mitigation (Bernauer and McGrath, 2016; Fesenfeld and Rinscheid, 2021). If there are any effects, they are likely to be small and have to compete with counter frames that are present in public and media discourses (Boykoff, 2014; O’Neill et al., 2015; Stoddart et al., 2023).
The results suggest that spelling out policy costs may have a greater effect than mentioning the co-benefits. This may be because of the direct cost implications (making the policies less attractive) or because mentioning the implications may make the policy more personally relevant. Previous research shows that even mentioning a very modest cost can reduce climate policy support (Whitmarsh et al., 2019). This asymmetry in cost–benefit framing is in line with the well-established prospect theory (Kahneman and Tversky, 1979) and has important implications for communication (see below). The one exception is environmental pricing, for which support is higher when potential lifestyle implications are mentioned. A possible explanation for this surprising effect is that people had already taken into account those potential implications of the policy.
A series of regression analyses showed that there were some differences in support for the eight net zero policies across different socio-demographic groups, but the effects were not consistent. Overall, net zero policies were found to be more supported by women and older age groups. Other notable results were that that LTNs are supported less in London, and that certain net zero policies are supported less by minority ethnic backgrounds living in more deprived neighbourhoods. These inconsistent findings may be because demographic factors only partially map on to people’s needs and abilities, with more direct effects on policy support from perceived policy fairness (cf. Player et al., 2023).
Stronger effects were found for individual values and beliefs than for socio-demographic factors, with effects also more consistent across the eight net zero policies. That is, people who are worried about climate change – perhaps unsurprisingly – express higher levels of support for all eight policies, as do those with more left-wing (versus right wing) and libertarian (versus authoritarian) political values. These results are in line with a substantial body of empirical and theoretical research showing that problem perception (climate concern) is one of the most important determinants of (climate) policy support (Poortinga et al., 2012; Drews and van den Bergh, 2016; Bouman et al., 2020; Bergquist et al., 2022); and that political orientation (e.g., left versus right, liberal versus conservative) shapes beliefs about climate in particular in anglophone countries (Hornsey et al., 2018; Poortinga et al., 2019), including for climate policies (Poortinga et al., 2012, 2022; Ejelöv and Nilsson, 2020; Bergquist et al., 2022).
The strongest and most consistent predictor of net zero support was, however, perceived fairness. The results fit well with the literature showing perceived fairness is a key driver of policy support (Maestre-Andrés et al., 2019; Climate Assembly UK, 2020; Ejelöv and Nilsson, 2020; Liu et al., 2020; Bergquist et al., 2022). Our measure of perceived fairness encompasses distributional and procedural elements, both of which are known to be important for policy support; but our other findings suggest wider interpretations of fairness may be at play. The relative popularity of frequent flyer levies and environmental fee-dividend pricing may be due to these policies reflecting the ‘polluter pays’ principle (i.e., fair distribution of costs) but also conserving freedom of choice; while our findings that personal cost reduces support may also be taken as form of perceived unfairness for the individual (Webster et al., 2022). Notably, perceptions of fairness may be constructed post-hoc to justify or reinforce intuitive policy preferences; that is, people inclined to support net zero policies (e.g., due to climate concern) may align their policy evaluations (e.g., of fairness) with this support (Zajonc, 1980).
Strengths and limitations
The main strength of the current study is that it made use of a high-quality probability sample collected by a professional social survey company (Ipsos, 2022). The sample is large enough to be able to partition the survey to help reduce the burden on the respondents and thus to maintain response quality. Random probability sampling is the gold standard of survey research and can be used to make robust population and regression estimates (Thompson, 2012). The wide range of policies examined was also a strength and point of novelty. A further strength of the study is that it used policies that are already enacted or proposed to be used in the UK. This was done so that participants could easily envisage them and thus have or form an opinion about them, but also to ensure that the results of the study can be used by policymakers who are responsible for designing and implementing net zero.
As any study, it also has a number of limitations. It was for example not possible to include a larger number of policies. Ideally, follow-up research would include different types of policies (e.g., subsidies, taxes, regulation, information) systematically across the different behavioural domain to be able to reliably apportion variance in support to those different policy characteristics (cf., Poortinga et al., 2022). This would be able to show for example whether ‘pull’ measures are always preferred over ‘push’ measures (Steg et al., 2006), or whether taxes are more acceptable in certain behavioural domains but not in others. Carbon taxes are generally disliked (Maestre-Andrés et al., 2019; Umit and Schaffer, 2020), but frequent flyer levies, also a tax, was the most supported policy in this study. Other limitations relate to the framing and the questions to determine the impacts of potential cost and lifestyle implications of net zero policies. The specific effects depend on the way information is presented, and it is therefore possible that the relatively small framing effects are because the frames are not powerful enough (cf., Bernauer and McGrath, 2016). In contrast, the potential implications used to determine the conditional support for the different net zero policies (see Supplementary Information Table SI2) may never materialise. Nevertheless, results showing high levels of support based on generic policy descriptions may miss the nuances and conditionality of such support (Demski, 2011). A related limitation was that the study only allowed the inclusion of a limited number of co-benefit frames. A main finding of Bain et al. (2016) was that the social benefits (‘benevolence’) can motivate action on climate change. It may therefore be interesting to include such social benefits of climate policy to cover all pillars of sustainable development. The inclusion of social co-benefits of action may help strengthen the results showing that perceived fairness as the most important predictor of net zero policy support. It seems to us that this is a limitation of the study that should be discusses.
Conclusion and policy implications
The main finding of this study is that the UK public are generally supportive of net zero, with the results showing that there is a high level of support for a variety of policies that can be used to establish change in the behavioural domains of travel, diet, material and energy consumption, and financial investment. The public appear to support net zero policies slightly more if they are framed in terms of their health, economic and climate change benefits, but these effects are small. This suggests that, in line with other research, a simple reframing is unlikely to lead to massive changes in support, although it may still be used to create awareness of the wider benefits of net zero policies among less committed publics (Bain et al., 2016).
While support for net zero appears robust, results from this study suggest that this may drop sharply when potential cost implications are presented. This may mean that public support for net zero policies is potentially fragile. Policymakers need to understand the that where the general public have concerns about the cost and lifestyle implications of net zero policies, support for these policies may change. Simply ignoring potential personal costs when introducing policies is likely to create problems when these come to light.
Perceived fairness has been found to be the strongest predictor of policy support, and the way costs and lifestyle implications (are perceived to) play out across different groups is likely to be a core factor in net zero policy support. Indeed, arguments against – for example – ultra-low emission zones (ULEZs) and low-traff eighbourhoods (LTNs) are often phrased in terms of how unfair they are for specific groups (BBC, 2023a,b). Even if distributional effects may be counter to the claims made by those opposing the policy (Aldred et al., 2021; Yang et al., 2022), such arguments can be persuasive and thus lead to lower support (see, e.g., Ipsos & CAST, 2022).
The overall conclusion is that the public are supportive of net zero polies in the UK, but that this support cannot be taken for granted. The public are more likely to be supportive of net zero if and when they feel they are fair in terms of the decision-making process and their outcomes. A comprehensive and inclusive public engagement strategy may be needed that takes into account citizens’ needs and concerns to build a mandate for action (Verfuerth et al., 2023). This may help to avoid public backlash when policies are implemented.
Data availability statement
The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.
Ethics statement
The studies involving humans were approved by School of Psychology Research Ethics Committee. The studies were conducted in accordance with the local legislation and institutional requirements. The participants provided their written informed consent to participate in this study.
Author contributions
WP: Conceptualization, Writing – original draft, Writing – review & editing, Formal analysis. LW: Conceptualization, Writing – original draft, Writing – review & editing. KS: Writing – review & editing, Conceptualization. EG: Conceptualization, Data curation, Project administration, Writing – review & editing. ST: Conceptualization, Data curation, Project administration, Writing – review & editing. RB: Conceptualization, Data curation, Project administration, Writing – review & editing.
Funding
The author(s) declare financial support was received for the research, authorship, and/or publication of this article. We acknowledge support from the Economic & Social Research Council (ESRC) through the Centre for Climate Change and Social Transformations (CAST), Grant Ref: ES/S012257/1. The research was conducted as part of the Ipsos-CAST Climate Engagement Partnership.
Conflict of interest
EG, ST and RB are employed by Ipsos UK.
The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
Supplementary material
The Supplementary material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fpsyg.2023.1287188/full#supplementary-material
References
Akenji, L., Bengtsson, M., Toivio, V., Lettenmeier, M., Fawcett, T., Parag, T., et al. (2021). 1.5-degree lifestyles: towards a fair consumption space for all. Berlin: Hot or Cool Institute.
Aldred, R. (2019). Who caused that congestion? Narrating driving and cycling in a changing policy context. Travel Behav Soc 16, 59–69. doi: 10.1016/j.tbs.2019.04.004
Aldred, R., Verlinghieri, E., Sharkey, M., Itova, I., and Goodman, A. (2021). Equity in new active travel infrastructure: a spatial analysis of London’s new low traffic neighbourhoods. J Transp Geogr 96:103194. doi: 10.1016/j.jtrangeo.2021.103194
Bain, P. G., Milfont, T. L., Kashima, Y., Bilewicz, M., Doron, G., Garðarsdóttir, R. B., et al. (2016). Co-benefits of addressing climate change can motivate action around the world. Nat Clim Chang 6, 154–157. doi: 10.1038/nclimate2814
Baranzini, A., and Carattini, S. (2017). Effectiveness, earmarking and labeling: testing the acceptability of carbon taxes with survey data. Environ Econ Policy Stud 19, 197–227. doi: 10.1007/s10018-016-0144-7
Bates, D., Mächler, M., Bolker, B., and Walker, S. (2015). Fitting linear mixed-effects models using lme4. J Stat Softw 67, 1–48. doi: 10.18637/jss.v067.i01
BBC. (2023a). ULEZ expansion: London emission zone ‘extremely unfair’ for Kent drivers. Available at: https://www.bbc.co.uk/news/uk-england-kent-64541632
BBC. (2023b). ULEZ: London mayor lacks powers to expand zone, High Court told. Available at: https://www.bbc.co.uk/news/uk-england-london-66094244
Bechtel, M. M., and Scheve, K. F. (2013). Mass support for global climate agreements depends on institutional design. Proc Natl Acad Sci 110, 13763–13768. doi: 10.1073/pnas.1306374110
Bergquist, M., Nilsson, A., Harring, N., and Jagers, S. C. (2022). Meta-analyses of fifteen determinants of public opinion about climate change taxes and laws. Nat Clim Chang 12, 235–240. doi: 10.1038/s41558-022-01297-6
Bernauer, T., and McGrath, L. F. (2016). Simple reframing unlikely to boost public support for climate policy. Nat Clim Chang 6, 680–683. doi: 10.1038/nclimate2948
Besley, J. C. (2010). Public engagement and the impact of fairness perceptions on decision favorability and acceptance. Forensic Sci Commun 32, 256–280. doi: 10.1177/1075547009358624
Bouman, T., Verschoor, M., Albers, C. J. C. J., Boehm, G., Fisher, S. D. S. D., Poortinga, W., et al. (2020). When worry about climate change leads to climate action: how values, worry and personal responsibility relate to various climate actions. Glob Environ Chang 62, 1–11. doi: 10.1016/j.gloenvcha.2020.102061
Boykoff, M. T. (2014). Media discourse on the climate slowdown. Nat Clim Chang 4, 156–158. doi: 10.1038/nclimate2156
Cai, B., Cameron, T. A., and Gerdes, G. R. (2010). Distributional preferences and the incidence of costs and benefits in climate change policy. Environ Resource Econ 46, 429–458. doi: 10.1007/s10640-010-9348-7
Campbell, M. (2023). “Messaging, emergencies, and public Disontent: implementing active travel initiatives during COVID-19” in Public participation in transport in times of change, vol. 18 (UK: Emerald Publishing Limited), 117–136.
Carmichael, R. (2019). Behaviour change, public engagement and net zero. A report for the committee on climate change. London: Imperial College London.
Climate Assembly UK. (2020). The path to net zero: Climate assembly UK full report. UK: UK Parliament.
Climate Change Committee. (2020). The Sixth Carbon Budget: The UK’s path to Net Zero. Climate Change Committee. Available at: www.theccc.org.uk/publication/sixth-carbon-budget
Creutzig, F., Niamir, L., Bai, X., Callaghan, M., Cullen, J., Díaz-José, J., et al. (2022). Demand-side solutions to climate change mitigation consistent with high levels of well-being. Nat Clim Chang 12, 36–46. doi: 10.1038/s41558-021-01219-y
Dechezleprêtre, A., Fabre, A., Kruse, T., Planterose, B., Chico, A. S., and Stantcheva, S. (2022). Fighting climate change: International attitudes toward climate policies. Cambridge, Massachusetts: National Bureau of Economic Research.
Demski, C. (2011). Public perceptions of renewable energy technologies: Challenging the notion of widespread support. Cardiff University. Available at: https://orca.cardiff.ac.uk/id/eprint/13562
Dieplinger, M., and Fürst, E. (2014). The acceptability of road pricing: evidence from two studies in Vienna and four other European cities. Transp Policy 36, 10–18. doi: 10.1016/j.tranpol.2014.06.012
Drews, S., and van den Bergh, J. C. J. M. (2016). What explains public support for climate policies? A review of empirical and experimental studies. Clim Pol 16, 855–876. doi: 10.1080/14693062.2015.1058240
Dreyer, S. J., and Walker, I. (2013). Acceptance and support of the Australian carbon policy. Soc Justice Res 26, 343–362. doi: 10.1007/s11211-013-0191-1
Dudley, G., Banister, D., and Schwanen, T. (2022). Low traffic neighbourhoods and the paradox of UK government control of the active travel agenda. Polit Q 93, 585–593. doi: 10.1111/1467-923X.13198
Ejelöv, E., and Nilsson, A. (2020). Individual factors influencing acceptability for environmental policies: a review and research agenda. Sustainability 12:2404. doi: 10.3390/su12062404
Eliasson, J., and Jonsson, L. (2011). The unexpected “yes”: explanatory factors behind the positive attitudes to congestion charges in Stockholm. Transp Policy 18, 636–647. doi: 10.1016/j.tranpol.2011.03.006
Eriksson, L., Garvill, J., and Nordlund, A. M. (2008). Acceptability of single and combined transport policy measures: the importance of environmental and policy specific beliefs. Transp Res A Policy Pract 42, 1117–1128. doi: 10.1016/j.tra.2008.03.006
Evans, G., Heath, A., and Lalljee, M. (1996). Measuring left-right and libertarian-authoritarian values in the British electorate. Br J Sociol 47, 93–112. doi: 10.2307/591118
Fankhauser, S., Smith, S. M., Allen, M., Axelsson, K., Hale, T., Hepburn, C., et al. (2022). The meaning of net zero and how to get it right. Nat Clim Chang 12, 15–21. doi: 10.1038/s41558-021-01245-w
Fesenfeld, L. P., and Rinscheid, A. (2021). Emphasizing urgency of climate change is insufficient to increase policy support. One Earth 4, 411–424. doi: 10.1016/j.oneear.2021.02.010
Fujii, S., Gärling, T., Jakobsson, C., and Jou, R.-C. (2004). A cross-country study of fairness and infringement on freedom as determinants of car owners’ acceptance of road pricing. Transportation 31, 285–295. doi: 10.1023/B:PORT.0000025395.17250.49
Greenberg, J. (1986). Determinants of perceived fairness of performance evaluations. J Appl Psychol 71, 340–342. doi: 10.1037/0021-9010.71.2.340
Grubb, M., Crawford-Brown, D., Neuhoff, K., Schanes, K., Hawkins, S., and Poncia, A. (2020). Consumption-oriented policy instruments for fostering greenhouse gas mitigation. Clim Pol 20, S58–S73. doi: 10.1080/14693062.2020.1730151
Hammar, H., and Jagers, S. C. (2007). What is a fair CO2 tax increase? On fair emission reductions in the transport sector. Ecol Econ 61, 377–387. doi: 10.1016/j.ecolecon.2006.03.004
Höppner, C., and Whitmarsh, L. (2012). “Public engagement in climate action: policy and public expectations,” in Engaging the public with climate change. eds. L. Whitmarsh, S. O’Neill, and I. Lorenzoni (Routledge), 47–65.
Hornsey, M. J., Harris, E. A., and Fielding, K. S. (2018). Relationships among conspiratorial beliefs, conservatism and climate scepticism across nations. Nat Clim Chang 8, 614–620. doi: 10.1038/s41558-018-0157-2
House of Lords (2022). In our hands: Behaviour change for climate and environmental goals (1st report of session 2022–23). London: House of Lords Environment and Climate Change Committee.
Howarth, C., Morse-Jones, S., Kythreotis, A., Brooks, K., and Lane, M. (2020). Informing UK governance of resilience to climate risks: improving the local evidence-base. Clim Change 163, 499–520. doi: 10.1007/s10584-020-02821-3
IPCC. (2021). Climate change 2021: The physical science basis. Contribution of working group I to the sixth assessment report of the intergovernmental panel on climate change. Cambridge: Cambridge University Press.
IPCC. (2022). Climate change 2022: Mitigation of climate change. Contribution of working group III to the sixth assessment report of the intergovernmental panel on climate change. Cambridge: Cambridge University Press.
Ipsos. (2022). UK knowledge panel. Total understanding of the UK public. Ipos. Available at: https://www.ipsos.com/sites/default/files/2022-04/ipsos-uk-knowledgepanel-brochure.pdf
Ipsos. (2023). Earth Day 2023. Public opinion on climate change. Ipsos. Available at: https://www.ipsos.com/sites/default/files/ct/news/documents/2023-04/Ipsos%20Global%20Advisor%20-%20Earth%20Day%202023%20-%20Full%20Report%20-%20WEB.pdf
Ipsos & CAST. (2022). Net Zero living. Ipsos and Centre for Climate Change and Social Transformations (CAST). Available at: https://www.ipsos.com/sites/default/files/ct/publication/documents/2022-06/net-zero-living-ipsos-cast-2022.pdf
Ivanova, D., Barrett, J., Wiedenhofer, D., Macura, B., Callaghan, M., and Creutzig, F. (2020). Quantifying the potential for climate change mitigation of consumption options. Environ Res Lett 15:093001. doi: 10.1088/1748-9326/ab8589
Jakobsson, C., Fujii, S., and Gärling, T. (2000). Determinants of private car users’ acceptance of road pricing. Transp Policy 7, 153–158. doi: 10.1016/S0967-070X(00)00005-6
Jennings, N., Fecht, D., and De Matteis, S. (2020). Mapping the co-benefits of climate change action to issues of public concern in the UK: a narrative review. Lancet Planetary Heal 4, e424–e433. doi: 10.1016/S2542-5196(20)30167-4
Kahneman, D., and Tversky, A. (1979). Prospect theory: an analysis of decision under risk. Econometrica 47, 263–291. doi: 10.2307/1914185
Kim, J., Schmöcker, J.-D., Fujii, S., and Noland, R. B. (2013). Attitudes towards road pricing and environmental taxation among US and UK students. Psychol Sustain Travel Behav 48, 50–62. doi: 10.1016/j.tra.2012.10.005
Liu, L., Bouman, T., Perlaviciute, G., and Steg, L. (2020). Public participation in decision making, perceived procedural fairness and public acceptability of renewable energy projects. Energy and Climate Change 1:100013. doi: 10.1016/j.egycc.2020.100013
Lockwood, M. (2011). Does the framing of climate policies make a difference to public support? Evidence from UK marginal constituencies. Clim Pol 11, 1097–1112. doi: 10.1080/14693062.2011.579301
Maestre-Andrés, S., Drews, S., and van den Bergh, J. (2019). Perceived fairness and public acceptability of carbon pricing: a review of the literature. Clim Pol 19, 1186–1204. doi: 10.1080/14693062.2019.1639490
Michielsen, Y. J. E., and van der Horst, H. M. (2022). Backlash against meat curtailment policies in online discourse: populism as a missing link. Appetite 171:105931. doi: 10.1016/j.appet.2022.105931
Morton, B. (2020). Will pop-up bike lanes keep new cyclists on the road? BBC News. Available at: https://www.bbc.com/news/uk-53105020
Nielsen, K. S., Stern, P. C., Dietz, T., Gilligan, J. M., van Vuuren, D. P., Figueroa, M. J., et al. (2020). Improving climate change mitigation analysis: a framework for examining feasibility. One Earth 3, 325–336. doi: 10.1016/j.oneear.2020.08.007
O’Neill, S., Williams, H. T. P., Kurz, T., Wiersma, B., and Boykoff, M. (2015). Dominant frames in legacy and social media coverage of the IPCC fifth assessment report. Nature. Clim Change 5, 380–385. doi: 10.1038/nclimate2535
Pechey, R., Reynolds, J. P., Cook, B., Marteau, T. M., and Jebb, S. A. (2022). Acceptability of policies to reduce consumption of red and processed meat: a population-based survey experiment. J Environ Psychol 81:101817. doi: 10.1016/j.jenvp.2022.101817
Player, L., Prosser, A. M. B., Thorman, D., Tirion, A. S. C., Whitmarsh, L., Kurz, T., et al. (2023). Quantifying the importance of socio-demographic, travel-related, and psychological predictors of public acceptability of low emission zones. J Environ Psychol 88:101974. doi: 10.1016/j.jenvp.2023.101974
Poortinga, W., Latter, B., and Wang, S. (2022). Comparing coronavirus (COVID-19) and climate change perceptions: implications for support for individual and collective-level policies. Front Psychol 13:996546. doi: 10.3389/fpsyg.2022.996546
Poortinga, W., Spence, A., Demski, C., and Pidgeon, N. F. N. F. (2012). Individual-motivational factors in the acceptability of demand-side and supply-side measures to reduce carbon emissions. Energy Policy 48, 812–819. doi: 10.1016/j.enpol.2012.06.029
Poortinga, W., Whitmarsh, L., Steg, L., Böhm, G., and Fisher, S. (2019). Climate change perceptions and their individual-level determinants: a cross-European analysis. Glob Environ Chang 55, 25–35. doi: 10.1016/j.gloenvcha.2019.01.007
Revelle, W. (2022). Package ‘psych’. Available at: https://cran.r-project.org/web/packages/psych/psych.pdf
Roberts, C., Geels, F. W., Lockwood, M., Newell, P., Schmitz, H., Turnheim, B., et al. (2018). The politics of accelerating low-carbon transitions: towards a new research agenda. Energy Res Soc Sci 44, 304–311. doi: 10.1016/j.erss.2018.06.001
Rossa-Roccor, V., Giang, A., and Kershaw, P. (2021). Framing climate change as a human health issue: enough to tip the scale in climate policy? Lancet Planetary Heal 5, e553–e559. doi: 10.1016/S2542-5196(21)00113-3
Schmöcker, J.-D., Pettersson, P., and Fujii, S. (2012). Comparative analysis of proximal and distal determinants for the acceptance of coercive charging policies in the UK and Japan. Int J Sustain Transp 6, 156–173. doi: 10.1080/15568318.2011.570856
Schuitema, G., Hooks, T., and McDermott, F. (2020). Water quality perceptions and private well management: the role of perceived risks, worry and control. J Environ Manage 267:110654. doi: 10.1016/j.jenvman.2020.110654
Schwirplies, C., Dütschke, E., Schleich, J., and Ziegler, A. (2019). The willingness to offset CO2 emissions from traveling: findings from discrete choice experiments with different framings. Ecol Econ 165:106384. doi: 10.1016/j.ecolecon.2019.106384
Shaw, C., Hales, S., Howden-Chapman, P., and Edwards, R. (2014). Health co-benefits of climate change mitigation policies in the transport sector. Nat Clim Chang 4, 427–433. doi: 10.1038/nclimate2247
Sievert, K., Lawrence, M., Parker, C., Russell, C. A., and Baker, P. (2022). Who has a beef with reducing red and processed meat consumption? A media framing analysis. Public Health Nutr 25, 578–590. doi: 10.1017/S1368980021004092
Smith, A. C., Holland, M., Korkeala, O., Warmington, J., Forster, D., ApSimon, H., et al. (2016). Health and environmental co-benefits and conflicts of actions to meet UK carbon targets. Clim Pol 16, 253–283. doi: 10.1080/14693062.2014.980212
Springmann, M., Godfray, H. C. J., Rayner, M., and Scarborough, P. (2016). Analysis and valuation of the health and climate change cobenefits of dietary change. Proc Natl Acad Sci 113, 4146–4151. doi: 10.1073/pnas.1523119113
Steentjes, K., Poortinga, W., Demski, C., and Whitmarsh, L. (2021). UK perceptions of climate change and lifestyle changes. CAST Briefing Paper 08. Available at: https://cast.ac.uk/wp-content/uploads/2021/03/CAST-Briefing-08.pdf
Steg, L., Dreijerink, L., and Abrahamse, W. (2006). Why are energy policies acceptable and effective? Environ Behav 38, 92–111. doi: 10.1177/0013916505278519
Stern, P. C. (2000). Toward a coherent theory of environmentally significant behavior. Aust J Soc Issues 56, 407–424. doi: 10.1111/0022-4537.00175
Stern, P. C., and Dietz, T. (2008). Public participation in environmental assessment and decision making. National Academies Press, Washington, DC.
Stoddart, M. C. J., Ramos, H., Foster, K., and Ylä-Anttila, T. (2023). Competing crises? Media coverage and framing of climate change during the COVID-19 pandemic. Environ Commun 17, 276–292. doi: 10.1080/17524032.2021.1969978
UK Government. (2019). The climate change act 2008 (2050 target amendment) order 2019. UK: The Stationery Office.
UK Government. (2023). Low-emission vehicles eligible for a plug-in grant. UK Government. Available at: https://www.gov.uk/plug-in-vehicle-grants
Umit, R., and Schaffer, L. M. (2020). Attitudes towards carbon taxes across Europe: the role of perceived uncertainty and self-interest. Energy Policy 140:111385. doi: 10.1016/j.enpol.2020.111385
Verfuerth, C., Demski, C., Capstick, S., Whitmarsh, L., and Poortinga, W. (2023). A people-centred approach is needed to meet net zero goals. J British Academy 11, 97–124. doi: 10.5871/jba/011s4.097
Webster, R., Powell, A., and Corner, A. (2022). Fairness’ in UK climate advocacy: A user’s guide. Oxford: Climate Outreach.
Whitmarsh, L. (2009). What’s in a name? Commonalities and differences in public understanding of “climate change” and “global warming”. Public Underst Sci 18, 401–420. doi: 10.1177/0963662506073088
Whitmarsh, L., and Corner, A. (2017). Tools for a new climate conversation: a mixed-methods study of language for public engagement across the political spectrum. Glob Environ Chang 42, 122–135. doi: 10.1016/j.gloenvcha.2016.12.008
Whitmarsh, L., Poortinga, W., and Capstick, S. (2021). Behaviour change to address climate change. Curr Opin Psychol 42, 76–81. doi: 10.1016/j.copsyc.2021.04.002
Whitmarsh, L., Xenias, D., and Jones, C. R. (2019). Framing effects on public support for carbon capture and storage. Palgrave Commun 5:17. doi: 10.1057/s41599-019-0217-x
Wickham, H., Averick, M., Bryan, J., Chang, W., McGowan, L. D., François, R., et al. (2019). Welcome to the Tidyverse. J Open Source Software 4:1686. doi: 10.21105/joss.01686
Wynes, S., and Nicholas, K. A. (2017). The climate mitigation gap: education and government recommendations miss the most effective individual actions. Environ Res Lett 12:074024. doi: 10.1088/1748-9326/aa7541
Wynes, S., Zhao, J., and Donner, S. D. (2020). How well do people understand the climate impact of individual actions? Clim Change 162, 1521–1534. doi: 10.1007/s10584-020-02811-5
Yang, X., McCoy, E., Hough, K., and de Nazelle, A. (2022). Evaluation of low traffic neighbourhood (LTN) impacts on NO2 and traffic. Transp Res Part D: Transp Environ 113:103536. doi: 10.1016/j.trd.2022.103536
Zajonc, R. B. (1980). Feeling and thinking: preferences need no inferences. Am Psychol 35, 151–175. doi: 10.1037/0003-066X.35.2.151
Keywords: net zero, climate change, policy support, framing effects, perceived fairness
Citation: Poortinga W, Whitmarsh L, Steentjes K, Gray E, Thompson S and Brisley R (2023) Factors and framing effects in support for net zero policies in the United Kingdom. Front. Psychol. 14:1287188. doi: 10.3389/fpsyg.2023.1287188
Edited by:
Louise Eriksson, Umeå University, SwedenReviewed by:
Christine Boomsma, National Institute for Public Health and the Environment, NetherlandsChristophe Demarque, Aix-Marseille Université, France
Copyright © 2023 Poortinga, Whitmarsh, Steentjes, Gray, Thompson and Brisley. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Wouter Poortinga, UG9vcnRpbmdhV0BjYXJkaWZmLmFjLnVr