Edited by: Fanli Jia, Seton Hall University, United States
Reviewed by: Susan Alisat, Wilfrid Laurier University, Canada; Enric Pol, University of Barcelona, Spain
This article was submitted to Environmental Psychology, a section of the journal Frontiers in Psychology
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This paper explores the public perception of energy transition pathways, that is, individual behaviors, political strategies, and technologies that aim to foster a shift toward a low-carbon and sustainable society. We employed affective image analysis, a structured method based on free associations to explore positive and negative connotations and affective meanings. Affective image analysis allows to tap into affective meanings and to compare these meanings across individuals, groups, and cultures. Data were collected among university students in Norway (
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Energy transition commonly refers to “a change in the state of an energy system as opposed to a change in an individual energy technology or fuel source” (
This paper investigates the public perception of energy transition pathways, with a focus on subjective mental representations in the form of connotative meanings and affective images. These meanings and images have been shown to play an important part in shaping public perceptions and responses to societal risk issues such as climate change (
Energy transition is a multifaceted concept that involves a variety of dimensions (
A large body of research exists in environmental psychology on topics that have some relevance to energy, yet little research has taken a comprehensive look at the many facets of energy transition. One existing research field deals with specific individual energy sources, for example perception and acceptance of nuclear power (for reviews, see
We argue that if the aim is to study subjective mental representations of energy transition, a broad range of potential actions and changes need to be taken into account (see also
It is widely agreed that people’s subjective mental representations, or mental models, shape risk perceptions and play an important role in guiding behavior (
An expanding literature suggests that mental models can guide individual behavior and policy support, for instance in response to climate change (e.g.,
Mental models are not always detailed and elaborate, which may depend on how much a person knows and has thought about the issue in question. For global problems such as climate change, it has been found that people generally lack detailed conceptual understandings of the phenomenon (
The assumption is that new information is encoded based on some familiar concept (‘anchoring’,
It is increasingly recognized that information processing, risk perception, and decision-making are influenced by affect and emotions (
When it comes to research exploring public views on climate change, affective images have been linked with both risk perceptions and policy preferences.
Affective images stem from personal experiences on the one hand, and social discourses and media reporting on the other (
Our approach in studying public perceptions of energy transition extends prior research in several respects. First, in accordance with
Second, this study extends the existing literature by providing a comparison between two different cultural contexts, Norway and Germany, which differ in interesting ways with respect to their socio-political contexts and histories concerning energy systems (
We collected data in a Norwegian and a German sample. We employed affective image analysis (see below) in both samples, a structured method to explore connotative and affective meanings. Affective image analysis uses free associations and evaluations of these associations. We will compare these two elements of affective image analysis across the two samples.
Norwegian participants (
German participants (
Participants from both countries were informed about the topic and aims of the study, the anonymity of their answers, and the right to withdraw at any time from their participation. Consent of the participants was obtained by virtue of survey completion.
The main stimulus material consisted of 25 terms that describe actions that can be taken as part of a strategy toward sustainable ways of producing and using energy. We aimed to select a set of components that would cover a broad range of possible actions and include those that are relevant in the public’s mind as well as from a scientific and political perspective. We based the selection on four sources: (a) general desk research on the issue of energy transition, (b) desk research of the psychological and social science literature to identify environmental behaviors and policy options used in previous studies, (c) pilot interviews with students from the same target population as the participants in the current study, and (d) interviews with experts from the climate and political sciences. The components correspond in part to those used by
The 25 energy transition pathway components used in this study.
Label | Energy transition pathway component |
---|---|
appliances | Energy efficient home appliances (e.g., light bulbs) |
ccs | Carbon capture and storage |
compensate | Climate compensation (e.g., when buying flights) |
e.cars | Electric cars |
educ | Environmental education (e.g., in school, at work) |
engage | Political engagement |
flights | Avoid long flights |
houses | Energy efficient houses (e.g., geothermal heating) |
hydro | Hydropower |
int.agree | International agreements (e.g., on carbon emissions) |
int.trade | International trade with carbon offsets |
it | Information technologies (e.g., monitor home energy use) |
nuclear | Nuclear power |
pub.trans | Public transportation |
regulate | Regulations (e.g., laws to reduce sales of fossil fuel cars) |
saving | Energy saving (e.g., turn down heating) |
science | Science |
sharing | Sharing economy (e.g., carpooling) |
solar | Solar panels |
subsidy | Subsidies (e.g., for renewable energy) |
tax | Taxes (e.g., on carbon intensive goods and services) |
urban | Urban planning (e.g., car free zones) |
vegetar | Vegetarian food |
walking | Walking and cycling |
wind | Wind farms |
We followed a method described by Leiserowitz and colleagues (
For each energy transition pathway component, participants were asked to briefly describe the first thought that came to their minds with respect to this component. They were instructed to answer spontaneously and swiftly but without rushing. They gave their responses in writing in a free text field in the questionnaire.
After having completed the free association task, participants were requested to go through their free associations again and to indicate for each whether they considered it something positive, or negative, or neutral (neither positive nor negative). Responses were coded as +1, -1, or 0, respectively.
At the end of the questionnaire, participants were asked whether they had heard the term energy transition before participating in the study (yes/no). They were also asked to indicate their age, gender, and study program.
The free associations were content analyzed (
Distribution of the free associations across the categories of the coding scheme, aggregated across all energy transition pathway components, for Norwegian and German sample (percent).
Codes |
Category | Percentages Norway |
Percentages Germany | |||||||
---|---|---|---|---|---|---|---|---|---|---|
Label | Level 1 | Level 2 | Level 3 | Level 1 | Level 2 | Level 3 | Level 1 | Level 2 | Level 3 | |
R1.0 | 10 | 0 | 0.91 | |||||||
R1.1 | 11 | Requirement on international level | 1.32 | 1.30 | ||||||
R1.1.0 | 110 | 0.11 | 0.25 | |||||||
R1.1.1 | 111 | Need for international agreements | 0.72 | 0.53 | ||||||
R1.1.2 | 112 | Need for monitoring targets | 0.49 | 0.53 | ||||||
R1.2 | 12 | Requirement on the level of national policies | 9.51 | 9.77 | ||||||
R1.2.0 | 120 | 0.75 | 1.86 | |||||||
R1.2.1 | 121 | Regulation via incentives | 2.19 | 2.57 | ||||||
R1.2.2 | 122 | Regulation via punishments | 0.79 | 0.88 | ||||||
R1.2.3 | 123 | Need for facilitation (available infrastructure) | 3.66 | 2.64 | ||||||
R1.2.4 | 124 | Need to increase knowledge (fund research) | 2.11 | 1.83 | ||||||
R1.3 | 13 | Requirement on the level of the citizens within a society | 4.83 | 3.51 | ||||||
R1.3.0 | 130 | 0.04 | 0.07 | |||||||
R1.3.1 | 131 | Need to change behavior/lifestyles | 1.28 | 1.41 | ||||||
R1.3.2 | 132 | Need to change attitudes/values | 0.26 | 0.18 | ||||||
R1.3.3 | 133 | Need for collective action | 2.00 | 0.84 | ||||||
R1.3.4 | 134 | Need to increase awareness | 1.25 | 1.02 | ||||||
R2.0 | 20 | 0 | 1.09 | |||||||
R2.1 | 21 | Personal consequences | 6.45 | 6.11 | ||||||
R2.1.0 | 210 | 0.11 | 0.70 | |||||||
R2.1.1 | 211 | Personal time resources | 0.30 | 0.18 | ||||||
R2.1.2 | 212 | Personal financial resources | 2.49 | 2.35 | ||||||
R2.1.3 | 213 | Personal comfort | 1.47 | 1.37 | ||||||
R2.1.4 | 214 | Personal social interactions | 0.11 | 0.14 | ||||||
R2.1.5 | 215 | Personal health effects | 1.43 | 1.16 | ||||||
R2.1.6 | 216 | Personal freedom | 0.53 | 0.21 | ||||||
R2.2 | 22 | Societal consequences | 1.02 | 0.81 | ||||||
R2.2.0 | 220 | 0.04 | 0.21 | |||||||
R2.2.1 | 221 | Social risks | 0.08 | 0.07 | ||||||
R2.2.2 | 222 | Social justice | 0.91 | 0.53 | ||||||
R2.3 | 23 | Environmental consequences | 6.79 | 4.99 | ||||||
R2.3.0 | 230 | 3.55 | 0.25 | |||||||
R2.3.1 | 231 | Environmental pollution | 0.83 | 1.51 | ||||||
R2.3.2 | 232 | Environmental preservation | 1.32 | 2.85 | ||||||
R2.3.3 | 233 | Environmental aesthetics | 1.09 | 0.39 | ||||||
R3.0 | 30 | 0.60 | 1.62 | |||||||
R3.1 | 31 | Evaluation concerning feasibility | 3.36 | 4.85 | ||||||
R3.2 | 32 | Evaluation concerning effectiveness | 5.36 | 2.11 | ||||||
R3.3 | 33 | Evaluation concerning importance | 10.83 | 13.63 | ||||||
R3.3.0 | 330 | 8.72 | 11.52 | |||||||
R3.3.1 | 331 | Importance for the present | 0.30 | 0.25 | ||||||
R3.3.2 | 332 | Importance for the future | 1.81 | 1.86 | ||||||
R3.4 | 34 | Expression of skepticism | 4.00 | 7.77 | ||||||
R3.4.0 | 340 | 1.92 | 5.87 | |||||||
R3.4.1 | 341 | Skepticism toward underlying intentions | 1.55 | 1.83 | ||||||
R3.4.2 | 342 | Skepticism toward the scientific bases | 0.53 | 0.07 | ||||||
R3.5 | 35 | Expression of affective valence | 16.98 | 9.28 | ||||||
R3.5.0 | 350 | 0.19 | ||||||||
R3.5.1 | 351 | Positive affect | 14.08 | 6.99 | ||||||
R3.5.2 | 352 | Negative affect | 2.72 | 2.28 | ||||||
R3.6 | 36 | Expression of conflicting aspects | 7.85 | 9.98 | ||||||
R3.6.0 | 360 | 0.15 | 1.16 | |||||||
R3.6.1 | 361 | Conflict between different impacts | 7.66 | 8.75 | ||||||
R3.6.2 | 362 | Conflict between different generations | 0.04 | 0.07 | ||||||
R4.0 | 40 | 0.60 | 4.32 | |||||||
R4.1 | 41 | Prevalence with respect to personal actions | 1.17 | 3.65 | ||||||
R4.1.0 | 410 | 0.19 | 0.46 | |||||||
R4.1.1 | 411 | Respondent is already doing it | 0.75 | 2.39 | ||||||
R4.1.2 | 412 | Respondent lacks motivation | 0.23 | 0.81 | ||||||
R4.2 | 42 | Prevalence among certain social groups | 0.60 | 0.60 | ||||||
R4.2.0 | 420 | 0.19 | 0.25 | |||||||
R4.2.1 | 421 | Prevalence among certain subcultures | 0.19 | 0.28 | ||||||
R4.2.2 | 422 | Prevalence among demographic groups | 0.23 | 0.07 | ||||||
R5.1 | 51 | Mere description | 11.02 | 10.01 | ||||||
R5.2 | 52 | Non-codeable response | 2.68 | 2.28 | ||||||
R5.3 | 53 | Don’t know response | 5.02 | 1.41 | ||||||
The responses differ quite strongly in specificity. For example, some people said something like “that’s important” or “that’s good”; or, with respect to responses falling in the category of requirements, some participants said something like “won’t work on its own” very generally; while others were more specific and said something like “important to have binding agreements that include sanctions if they are broken.” In order to capture such differences in specificity, the coding scheme contains categories at three levels of specificity (see
In both samples, two university students coded the free associations. These were Norwegian native speakers for the Norwegian data and German native speakers for the German data. First, the two coders coded the responses independently. They were then asked to go through the responses on which they had disagreed and discuss whether they could solve the disagreement.
The Norwegian sample generated 2650 free associations. In their independent coding, coders agreed in 69.3% of these responses, Cohen’s Kappa = 0.674,
The German sample generated 2946 free associations. Intercoder-agreement was lower in the German than in the Norwegian sample. In their initial independent coding, the two coders agreed in 47.0% of the responses, Cohen’s Kappa = 0.446,
In Norway, data collection was done in a computer lab. Each participant was seated at an individual computer that was shielded by partitioning walls at the sides and at the front. Computer lab sessions were run in groups of 16 to 29 participants. All materials were presented and data collected via a computer-based survey (programmed in an online tool called Explorable
In Germany, data were collected by means of a paper-and-pencil questionnaire that was distributed at the end of lectures. The questionnaire consisted only of the free association and evaluation tasks (plus the background variables). Participants needed on average 20 min to fill in the questionnaire; they received a chocolate bar and a ballpoint pen as an incentive for their participation.
Participants were informed that the study dealt with the question of how people think and feel about various steps that can be taken as part of energy transition, which was defined as long-term changes in energy systems that aim at fostering a more sustainable society. The energy transition pathway components were then presented, each followed by an open text field on the computer screen (Norway) or a blank space on the paper questionnaire (Germany) for participants to fill in their free associations. Each participant received the components in one of two random orders. After participants had filled in their free associations, they were asked to evaluate them. In the computer-based procedure in Norway, participants were presented with their own free associations that they had entered before. In the paper-and-pencil based procedure in Germany, participants were asked to turn back in their questionnaire to evaluate their free associations. At the end of the questionnaire, participants had the opportunity to leave comments. Upon having completed the questionnaire, participants were thanked and received their incentive.
We will first focus on the content of the free associations and report the distributions of the free associations across the categories of the coding scheme. We then report the results concerning participants’ evaluations of their free associations. All statistical analyses were done using the R statistical environment (
The second most frequent categories, by a notable margin, are requirements and consequences, accounting for 13.00–15.66% of the free associations. Requirement means that the participant expressed some requirement needed to make a component work. These requirements often referred to national policies (e.g., necessary regulation or infrastructure; 9.51%, 9.77%) or, less often, to something required of the citizens in a society (e.g., lifestyle changes; 4.83%, 3.51%). Consequences means that the free association referred to a consequence of the energy transition pathway component, most often to personal consequences such as financial costs (6.45%, 6.11%) or to environmental consequences (6.79%, 4.99%).
The least frequent type of association referred to the prevalence of a component (2.38%, 8.57%). The remnant category comprises associations where the respondent either merely rephrased the component (the most frequent remnant category; 11.02%, 10.01), or responses that fit none of the categories (2.68%, 2.28%) or don’t know responses (5.02%, 1.41%).
In order to explore which types of free associations were generated with respect to which energy transition pathway component, we will consider only Level 1 codes from the coding scheme; the frequencies of the subcategories get too low when broken down across individual components.
Distribution of Level 1 codes for all energy transition pathway components, Norwegian data (percent).
Energy transition pathway component | Level 1 codes |
||||
---|---|---|---|---|---|
Requirements | Consequences | Evaluation | Prevalence | Remnant | |
appliances | 0.72 | 0.72 | 2.26 | 0.04 | 0.26 |
ccs | 0.15 | 0.11 | 1.32 | 0.00 | 2.42 |
compensate | 0.19 | 0.45 | 1.92 | 0.00 | 1.43 |
e.cars | 0.34 | 1.09 | 1.55 | 0.15 | 0.87 |
educ | 1.36 | 0.04 | 2.15 | 0.04 | 0.42 |
engage | 0.60 | 0.04 | 2.57 | 0.26 | 0.53 |
flights | 0.68 | 0.60 | 2.42 | 0.11 | 0.19 |
houses | 0.60 | 0.38 | 1.89 | 0.23 | 0.91 |
hydro | 0.45 | 0.75 | 1.25 | 0.11 | 1.43 |
int.agree | 1.09 | 0.15 | 2.23 | 0.00 | 0.53 |
int.trade | 0.34 | 0.60 | 2.19 | 0.00 | 0.87 |
it | 1.28 | 0.19 | 1.70 | 0.00 | 0.83 |
nuclear | 0.11 | 0.53 | 2.45 | 0.00 | 0.91 |
pub.trans | 1.66 | 0.79 | 1.17 | 0.19 | 0.19 |
regulate | 0.49 | 0.38 | 2.26 | 0.04 | 0.83 |
saving | 0.91 | 1.02 | 1.28 | 0.26 | 0.53 |
science | 0.38 | 0.11 | 2.57 | 0.00 | 0.94 |
sharing | 0.60 | 0.60 | 2.19 | 0.08 | 0.53 |
solar | 0.45 | 0.42 | 1.96 | 0.15 | 1.02 |
subsidy | 0.42 | 0.15 | 2.49 | 0.00 | 0.94 |
tax | 0.68 | 0.45 | 2.34 | 0.08 | 0.45 |
urban | 0.60 | 0.72 | 2.23 | 0.08 | 0.38 |
vegetar | 0.75 | 1.06 | 1.66 | 0.23 | 0.30 |
walking | 0.60 | 1.96 | 1.02 | 0.23 | 0.19 |
wind | 0.19 | 0.94 | 1.92 | 0.11 | 0.83 |
Distribution of Level 1 codes for all energy transition pathway components, German data (percent).
Energy transition pathway component | Level 1 codes |
||||
---|---|---|---|---|---|
Requirements | Consequences | Evaluation | Prevalence | Remnant | |
appliances | 0.98 | 0.60 | 1.76 | 0.53 | 0.35 |
ccs | 0.25 | 0.25 | 0.49 | 0.04 | 0.70 |
compensate | 0.53 | 0.49 | 1.51 | 0.25 | 0.88 |
e.cars | 0.42 | 0.60 | 2.35 | 0.35 | 0.67 |
educ | 0.63 | 0.07 | 2.28 | 0.88 | 0.49 |
engage | 0.63 | 0.39 | 1.83 | 0.88 | 0.32 |
flights | 0.14 | 0.70 | 2.71 | 0.49 | 0.28 |
houses | 0.56 | 0.74 | 2.04 | 0.35 | 0.46 |
hydro | 0.35 | 0.53 | 2.00 | 0.25 | 0.74 |
int.agree | 0.91 | 0.04 | 2.28 | 0.04 | 0.60 |
int.trade | 0.35 | 0.25 | 1.86 | 0.00 | 0.49 |
it | 0.35 | 0.56 | 2.35 | 0.18 | 0.63 |
nuclear | 1.23 | 0.28 | 2.18 | 0.00 | 0.67 |
pub.trans | 1.58 | 0.77 | 1.19 | 0.28 | 0.46 |
regulate | 0.70 | 0.32 | 2.32 | 0.07 | 0.74 |
saving | 1.02 | 0.46 | 1.37 | 0.95 | 0.56 |
science | 0.70 | 0.25 | 1.79 | 0.11 | 1.23 |
sharing | 0.39 | 0.91 | 2.11 | 0.67 | 0.32 |
solar | 0.63 | 0.42 | 1.62 | 0.56 | 0.95 |
subsidy | 0.63 | 0.25 | 2.35 | 0.14 | 0.42 |
tax | 0.53 | 0.49 | 2.46 | 0.00 | 0.35 |
urban | 0.49 | 0.49 | 2.57 | 0.11 | 0.46 |
vegetar | 0.42 | 0.98 | 2.14 | 0.60 | 0.18 |
walking | 0.60 | 1.44 | 1.41 | 0.77 | 0.18 |
wind | 0.46 | 0.74 | 2.25 | 0.11 | 0.60 |
Again, the two samples show a very similar pattern; this is indicated numerically by a high correlation between the Norwegian and the German frequencies across the cells of the cross-tabulation of Level 1 codes with energy transition pathway components (i.e., across the cells of
The relationship between type of free association, as captured by Level 1 codes, and energy transition pathway components was explored by means of a correspondence analysis (
Correspondence analysis plot of Level 1 code categories cross-tabulated with energy transition pathway components; common analysis of Norwegian and German data. Energy transition pathway components are labeled in lower-case letters and red font. Level 1 codes are labeled in blue font and upper-case letters; labels of Level 1 codes for the Norwegian sample end on “_Nor”, those for the German sample on “_Ger”. See
The corresponding Level 1 codes for the Norwegian and the German sample are located in close proximity to each other. Thus, the energy transition pathway components generated similar patterns of free associations in the two samples; as was already indicated by the high correlation between the two samples concerning Level 1 code frequencies across components. In order to interpret which types of free associations were generated for which energy transition pathway components, imagine for each component a line that connects the component with the origin of the coordinate system. The projection of a Level 1 code onto this imagined line indicates how closely this type of free association relates to the component.
Evaluation is located close to the origin, which indicates that evaluations are not specific for any particular component; they are generated frequently across all components. Evaluations are the most typical free association overall. Components in the lower left quadrant, especially walking, generated associations concerning consequences and prevalence. The remnant category is most closely associated with carbon capture and storage and also with carbon compensation; especially in Norway also with hydropower. Public transportation, environmental education, and international agreements elicit associations that reflect that people see them as needing further requirements, particularly in the Norwegian sample. Energy efficient houses is the energy transition pathway component that is most closely at the origin of the configuration, which indicates that it is the component whose pattern of free associations is most similar to the average pattern across all components. This could imply that energy efficient houses are the most prototypical energy transition pathway component in laypeople’s minds.
The horizontal dimension as a whole separates individual action on the left side (e.g., walking, vegetarian food, energy saving, public transport) from political-societal actions (in the upper half; e.g., science, subsidies, regulation) and technologies (in the lower half; e.g., CCS, nuclear-, solar-, hydropower) on the right. Individual actions are associated with prevalence, consequences, and requirements (especially Norway); political-societal actions and technologies elicited primarily descriptive associations (the predominant remnant category) and also more evaluations than average (in Norway).
Participants’ evaluations of their own free associations as either positive, neutral, or negative are summarized in
Average evaluation of free associations per energy transition pathway component.
Norwegian sample |
German sample |
|||||||||
---|---|---|---|---|---|---|---|---|---|---|
Energy transition pathway component | 95%CI lower limit | 95%CI upper limit | 95%CI lower limit | 95%CI upper limit | ||||||
appliances | 106 | 0.75 | 0.49 | 0.66 | 0.85 | 110 | 0.75 | 0.53 | 0.66 | 0.85 |
ccs | 106 | –0.04 | 0.60 | –0.15 | 0.08 | 54 | –0.67 | 0.48 | –0.79 | –0.54 |
compensate | 106 | 0.01 | 0.79 | –0.14 | 0.16 | 102 | 0.15 | 0.84 | –0.02 | 0.31 |
e.cars | 106 | 0.70 | 0.59 | 0.59 | 0.81 | 114 | 0.35 | 0.81 | 0.20 | 0.50 |
educ | 106 | 0.84 | 0.46 | 0.75 | 0.93 | 114 | 0.59 | 0.76 | 0.45 | 0.73 |
engage | 106 | 0.55 | 0.66 | 0.42 | 0.67 | 62 | 0.29 | 0.88 | 0.07 | 0.51 |
flights | 106 | –0.23 | 0.78 | –0.38 | –0.08 | 78 | –0.35 | 0.83 | –0.53 | –0.16 |
houses | 106 | 0.66 | 0.57 | 0.55 | 0.77 | 112 | 0.64 | 0.67 | 0.52 | 0.77 |
hydro | 106 | 0.82 | 0.43 | 0.74 | 0.90 | 57 | 0.30 | 0.78 | 0.10 | 0.50 |
int.agree | 106 | 0.35 | 0.77 | 0.20 | 0.50 | 69 | –0.16 | 0.87 | –0.36 | 0.05 |
int.trade | 106 | 0.02 | 0.85 | –0.14 | 0.18 | 94 | –0.56 | 0.60 | –0.68 | –0.44 |
it | 106 | 0.59 | 0.57 | 0.49 | 0.70 | 108 | 0.40 | 0.77 | 0.25 | 0.54 |
nuclear | 106 | –0.54 | 0.71 | –0.67 | –0.40 | 113 | –0.58 | 0.75 | –0.71 | –0.44 |
pub.trans | 106 | 0.54 | 0.76 | 0.39 | 0.68 | 114 | 0.54 | 0.73 | 0.41 | 0.68 |
regulate | 106 | 0.54 | 0.72 | 0.40 | 0.67 | 109 | 0.24 | 0.87 | 0.08 | 0.40 |
saving | 106 | 0.52 | 0.75 | 0.38 | 0.66 | 114 | 0.77 | 0.53 | 0.67 | 0.87 |
science | 106 | 0.83 | 0.42 | 0.75 | 0.91 | 109 | 0.72 | 0.49 | 0.62 | 0.81 |
sharing | 106 | 0.56 | 0.60 | 0.44 | 0.67 | 114 | 0.82 | 0.50 | 0.73 | 0.92 |
solar | 106 | 0.70 | 0.57 | 0.59 | 0.81 | 59 | 0.56 | 0.73 | 0.37 | 0.74 |
subsidy | 106 | 0.75 | 0.47 | 0.66 | 0.85 | 103 | 0.60 | 0.72 | 0.46 | 0.74 |
tax | 106 | 0.27 | 0.75 | 0.13 | 0.42 | 66 | 0.05 | 0.85 | –0.16 | 0.25 |
urban | 106 | 0.62 | 0.62 | 0.50 | 0.74 | 63 | 0.29 | 0.81 | 0.09 | 0.49 |
vegetar | 106 | 0.54 | 0.71 | 0.40 | 0.67 | 114 | 0.55 | 0.67 | 0.43 | 0.67 |
walking | 106 | 0.83 | 0.49 | 0.74 | 0.92 | 114 | 0.83 | 0.48 | 0.75 | 0.92 |
wind | 106 | 0.70 | 0.57 | 0.59 | 0.81 | 64 | 0.45 | 0.85 | 0.24 | 0.66 |
A graphical depiction of the average evaluations of the free associations for each energy transition pathway component is shown in
Scatterplot of participants’ evaluations of their own free associations, averaged across participants for each energy transition pathway component. Means for the Norwegian sample are plotted along the horizontal axis, those of the German sample along the vertical axis. See
If the free associations for a component are evaluated equally in both samples, the component lies on the diagonal. This is the case only for a few of the components. There is a general tendency of Norwegian participants to evaluate their free associations to the components more positively than German participants do. Exceptions are climate compensations, sharing economy, and energy saving, whose free associations are more positively evaluated in the German than in the Norwegian sample.
This study explored which mental images and affective evaluations laypeople associate with various energy transition pathway components, as have been described in the beginning of this paper. A remarkable result is the similarity between Norwegian and German participants despite differences in the socio-political contexts and traditions concerning energy. Considering studies showing that social representations are at least partly shaped by the socio-cultural context (
We drew quite homogeneous samples; namely, university students at both locations. While this homogeneity facilitates comparisons, it may have minimized variation in social and educational backgrounds. Some of the differences that exist between Norway and Germany concerning these countries’ socio-political energy contexts are presumably experienced more intensely in other socio-economic and professional groups than university students. A recent study showed, for instance, that employees in the Norwegian oil and gas industry tend to show less support for policies that restrict the production of fossil fuels than the larger population (
The most frequent type of free association was a general evaluation of the energy transition pathway component in response to which the association was generated. This most often referred to the level of importance assigned to each component, or to an affective evaluation of the component as something good or bad. Less often did the participants express that the component entails conflicting aspects, positive and negative, mostly referring to conflicting good and bad impacts. Other (less frequent) evaluations concerned the feasibility or effectiveness of the component or expressed some skepticism, for example concerning the trustworthiness of involved actors as well as their intentions. At a large interval from these evaluations, the second most frequent types of association are requirements needed to make a component work (usually some requirement at the level of national policies or individual actions), and consequences, typically personal consequences affecting finances or comfort or environmental consequences. About equally frequent as requirements and consequences were mere descriptions of the component or some aspect of it.
Rather than mentioning any detail that would hint at an elaborate mental representation of the components, the free associations generated by the participants suggest that knowledge about the presented pathway components is rather vague and unspecific. This matches prior studies indicating that people often hold a general pollution model according to which anything that pollutes the environment is also bad for the climate (
Nevertheless, people express clear evaluations of the components as good or bad, important or unimportant, effective or ineffective. One might assume that strong evaluations are based on knowledge; that people become more opposed or supportive of an issue, the more they know about it. The positive relationship between knowledge and polarization that has been found in the climate change literature supports this assumption (
When considering which types of association are generated in response to which energy transition pathway components, there seems to be a divide between individual actions, on one side, and socio-political actions and technologies, on the other side. This may indicate that people recognize the collective nature of energy transition, in addition to seeing individual behaviors as embedded in the societal context. It seems that with respect to individual actions people are most preoccupied with whether or not other people will join in and adopt the behavior (prevalence), what the personal consequences of the behavior are, whether the behavior is effective (environmental consequences), and that individual behavior depends on contextual conditions (requirements), such as the availability of public transport or other infrastructures. These three types of action seem to reflect a fundamental distinction in laypeople’s thinking about energy transition (for similar findings, see
By far the most negatively evaluated energy transition pathway component was nuclear power, whereas renewables such as solar-, wind-, and hydropower were located at the positive pole of evaluation. This resembles the pattern reported in another study that employed an affective image analysis with an explicit focus on energy sources (
An obvious limitation of this study concerns the small samples. Both samples were convenience samples, drawn from accessible pools of university students that cannot serve for drawing inferences regarding the wider public in each of the two countries. Although we do not claim to provide an international comparison, the results are very similar across the two countries, which suggests some stability. We therefore hope that our results have heuristic value and can guide future research in the study of the mental representation of energy transition pathways. We believe that the contents of the free associations as identified in our coding scheme give a good reflection of people’s concerns with respect to different energy transition pathways. We also believe that the cognitive structure of the components that emerged from the patterns of free associations connected to them and from the affective evaluation of these associations are worthy of further exploration in systematic survey and experimental research. The labor intense coding of the free associations precluded the use of larger samples in the present study. However, the emergence of new computer-based automated linguistic analysis techniques, such as structural topic models, may open up new avenues for collecting and analyzing free responses in large-scale surveys (see e.g.,
This empirical study complied with the Norwegian Social Science Data Services (NSD) privacy regulations and the ethical principles of research by the National Committee for Research Ethics in the Social Sciences and the Humanities (NESH). Formal approval from NSD was not sought, as the collected data material was anonymous, see
The raw data supporting the conclusions of this manuscript will be made available by the authors, without undue reservation, to any qualified researcher.
GB and RD contributed conception and design of the study. GB and H-RP performed the statistical analyses. GB wrote the first draft of the manuscript. GB, RD, and H-RP wrote sections of the manuscript. All authors contributed to manuscript revision, read and approved the submitted version.
The 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.
Data collection for the Norwegian sample was conducted at the computer lab (Citizen Lab) of the Digital Social Science Core Facility (DIGSSCORE) at the University of Bergen. We thank Annika Rødeseike for her assistance in developing study materials, organizing and conducting the lab sessions for the Norwegian data collection, and collecting the German data. We are grateful to Daniel Hansen, Lene Sævig, Sofie Antonsen, and Mai Emilie Ramdahl for their help in coding the open responses of the Norwegian sample, and to Sarah Stritzke and Anita Wieczorek, who assisted in data typing and coding of the open responses in the German sample. Preliminary analyses were presented at the ‘Beyond Oil’ conference at the University of Bergen in October 2017.
The Supplementary Material for this article can be found online at: