Abstract
The active promotion of carbon abatement to mitigate global climate change and protect the environment and public health has become the international consensus. The carbon capability is a key index for measuring the potential reduction of the carbon emissions by urban residents, and thus encouraging residents to exhibit normal and autonomous low-carbon behavior has become an important issue. In this study, based on grounded theory, data from in-depth interviews were encoded at three levels to identify the multi-layer factors that drive the carbon capability of urban residents, and we constructed a theoretical model for policy intervention. The results showed that individual factors, organizational factors, social factors, and social demographic variables were the main variables that affected the carbon capability, and utility experience perception was the main intermediary variable that affected the carbon capability. There was an obvious gap between utility experience perception and carbon capability. Low carbon selection cost was an internal situational variable that regulated the relationship between these factors, and the policy situation and technical situation were external situational variables. There were two-way effects on the carbon capability and utility experience perception. Thus, we explored these driving factors and the role of the carbon capability model. The results of this study may facilitate targeted policy thinking and the development of an implementation path for government in order to formulate effective guiding policies to enhance the carbon capability of urban residents.
1. Introduction
Global climate change is one of the most serious challenges facing mankind in the 21st century, where it influences the natural environment and the health and survival of humans and other organisms [,]. According to the “Global Climate Risk Index 2018”, more than 524,000 people have died worldwide as a direct result of over 11,000 extreme weather events []. It is well known that carbon dioxide emissions are the main cause of global warming. In addition, other pollutants such as sulfur dioxide and nitrogen dioxide are extremely harmful to public health [,,,]. Therefore, in order to protect the environment and public health, carbon emissions need to be reduced as soon as possible. The carbon emission intensity is most closely related to energy consumption. The U.S. Energy Information Agency estimated that global energy-related carbon emissions increased by 21% between 2005 and 2017, mainly from Asian countries such as China and India []. Energy-related carbon emissions are expected to remain relatively stable in most regions by 2019, but emissions from China are still increasing []. In June 2015, the Chinese government issued a statement regarding the intended nationally determined contributions (INDC), with a promise to reduce carbon emissions per unit of GDP by 60% by 2030 compared with 2005 []. In a context characterized by the comprehensive implementation of energy saving and emission reduction measures, energy consumption by industry has begun to achieve negative growth, but the consumption of domestic energy is increasing annually in the industrial sector, and the proportion of energy consumed has increased rapidly since 2010 []. According to the data in the Energy Statistics Yearbook, the per capita energy consumption by urban residents is much higher than that by rural residents, where the difference is as high as 3.5 times []. In addition, according to the “National New Urbanization Plan 2014–2020” issued by the State Council, the urbanization rate for China’s resident population will increase from 52.6% in 2013 to 60% in 2020 [], which means that the energy consumption by urban residents will continue to account for most of the overall energy consumed by residents. In addition, at present, China is still in a period of rapid industrialization and urbanization. Due to the sustained growth of the economy, life in the context of urbanization and the continuous changes in transportation modes mean that the energy consumption by urban residents and the resulting carbon emissions will increase further. Understanding how to exploit the potential low-carbon emission reductions by residents is an important issue for the development of low-carbon economy. Residents are the third largest producers of emissions after the government and enterprises, and thus the motivation and ability to reduce carbon emissions is important for social progress.
In this context, previous studies have explored the “carbon capability” concept to measure the motivation and potential of residents regarding reductions in their carbon emissions [,,]. The carbon capability refers to the “capability of individuals to make wise judgments about low carbon and take effective measures.” Previous studies have emphasized the need to consider knowledge, decisions, individual behaviors, and collective behaviors. Evidently, clear judgments and the effective implementation of low-carbon behaviors are core elements of the carbon capability, but the capacity for low-carbon behavior is not equal to the carbon capability itself. According to the classical theory of capability research, i.e., iceberg theory, capability is not confined only to knowledge and skills that comprise the superficial part above the sea level, i.e., the value concept. Instead, the motivation that lurks in the deep part below sea level is the key for distinguishing individual differences in capability [,,]. The capabilities of urban residents that can be observed easily, such as knowledge, skill, and behavior, are explicit features, but the elements lurking below sea level, such as low-carbon value concepts, are motivations that are deeply rooted in residents. These motivations are very important for understanding, evaluating, and improving the low-carbon capability. Wei et al. proposed the concept of the carbon capability []. The carbon capability of urban residents comprises an advanced set of abilities related to the overall process, which ranges from establishing the low carbon value concept, mastering the skills of low carbon identification, making wise low carbon choices, taking effective low carbon actions, and having a low carbon influence. The carbon capability is widely acknowledged as having five dimensions: carbon value, carbon identification, carbon choice, carbon mobility, and carbon impact. The concept of carbon capability maturity was subsequently proposed and it was suggested that an important premise for building guiding policies for developing the carbon capability is exploring the key factors responsible for driving the carbon capability, but these factors have been considered little in previous studies []. Several studies have focused on the carbon capability concept and standard measurements, but few have conducted specific analyses of the factors that affect the carbon capability. Thus, it is necessary to identify the drivers of carbon generation and development in order to guide and enhance the ability of urban residents to reduce carbon emissions effectively. Essentially, we need to identify the underlying psychological processes related to the carbon capability and understand how these psychological processes contribute to the transformation of low carbon cognition into low carbon behavior. In addition, we need to formulate effective intervention policies to shape and enhance the carbon capability, and ensure the acceptability and effectiveness of these interventions. These issues have not been addressed in previous theoretical studies.
Therefore, in this study, we aimed to describe, illustrate, and interpret the factors that drive the carbon capability of urban residents. We explored the main drivers of changes in the carbon capability of urban residents and the mechanisms related to these factors. We identified possible external intervention policies to promote the carbon capability of urban residents and the intervention path for these policies, as well as providing a theoretical basis and policy reference to help relevant government agencies formulate effective intervention policies.
2. Literature Review
Obtaining deep insights into the factors that influence the carbon capability of urban residents is important for exploring effective intervention policies. However, there have been few specific analyses of the factors that affect the carbon capability and only a few related studies have considered the capacity for low-carbon behavior. The low carbon consumption ability is regarded as the antecedent variable for low carbon consumption behavior. For example, Mi et al. regarded the “low carbon behavior ability” as a factor that influences “low carbon behavior willingness,” which directly affects the low-carbon energy consumption behavior of urban residents []. Given that the carbon capability is an actual ability, it is necessary to consider its characteristics and the factors that influence it. The factors that influence this ability are genetic, environmental, and non-intellectual (emotional processes, will processes, temperament, and personality) []. In addition, given that knowledge and skills are the cognitive basis of competence, and individual behavior is the carrier of capacity, then low-carbon knowledge/skills are the cognitive basis of low-carbon capability, and low-carbon consumer behavior is the result of carbon capability behavior. Therefore, it is necessary to review the theory of low-carbon knowledge/skills, low-carbon consumption behavior, and related research.
Many theoretical and empirical studies have investigated low-carbon consumption behavior, green consumption behavior, and other types of energy consumption behavior from different perspectives. These variables are not completely consistent with the low carbon consumption behavior in terms of their connotation and extension, but the conclusions of these studies provide a useful reference for low carbon consumption behavior. Previous studies have explored the key variables related to the mechanism of low-carbon consumption behavior in urban residents. However, studies of external factors such as subjective norms and social responsibility consciousness have mostly considered endogenous psychological factors, including the environmental attitude, environmental values, and other variables [], whereas few have investigated the key psychological variables related to deeper factor-personality traits. Personality is the core of individual beliefs, values, and attitudes. Many studies have shown that personality traits have significant impacts on environmental behavior [,]. Thus, differences in personality affect individual environmental attitudes and environmental behaviors []. Low carbon consumption behavior is an environmental behavioral concept, and thus personality traits may also affect the low carbon consumption behavior of individuals []. In addition, demographic variables can be employed to analyze the differences in the low-carbon consumption behaviors of urban residents [,,,], where these variables include gender, age, marital status, education, occupation, and income. In general, theoretical studies have focused on two areas: the factors that influence low-carbon consumption behavior and the internal mechanism involved; and intervention policies and their effectiveness at promoting low-carbon consumption behavior [,,]. The related factors include individual characteristics (such as age, occupation, income, and educational background), endogenous psychological factors, and exogenous situational factors. However, most previous studies focused on either the factors that influence low-carbon consumption behavior or intervention policies, whereas few have attempted to integrate both perspectives by exploring the determinants and intervention policies at the same time [].
In summary, studies of the variables that affect the carbon capability of urban residents are still very rare. There is a lack of in-depth research into the mechanisms and policy guidance path for the factors that influence the carbon capability. Therefore, based on previous research, we investigated the main factors that drive the carbon capability of urban residents and explored the policy guidance path.
3. Research Methods and Data Sources
3.1. Research Methods
The carbon capability of urban residents is not completely clear at present, and thus it is necessary to conduct exploratory qualitative research. Therefore, the exploratory method employed for data analysis in this study was mainly based on grounded theory. Grounded theory was proposed in 1967 [] and it is now regarded as “the most influential research paradigm in modern social science and at the forefront of the qualitative research revolution” [,,]. The original analysis of data in grounded theory was mostly based on written data. In this study, we recorded in-depth interviews with representative urban residents. The core idea of grounded theoretical analysis is continuous comparative analysis, which is embodied in the contents of a document before and after analysis, and between the data. The concepts and category elements related to the research goal can be found via continuous comparative analysis. Attributes can be generalized and the corresponding theory may be constructed from the bottom to the top. The specific steps in grounded theoretical analysis mainly include open coding, axial coding, and selective coding, as shown in Figure 1.
Figure 1.
Encoding process and overall qualitative research method.
Based on the process described above, we determined the main factors related to the carbon capability of urban residents, especially the factors that drive it and the mechanism responsible, before establishing the relationships between various concepts and category elements, and finally constructing a theoretical framework as a model of the mechanisms that drive the carbon capability of urban residents. The overall research process is illustrated schematically in Figure 1.
3.2. Data Collection
The first process in qualitative research is data collection. In this study, representative urban residents from the sample area were interviewed in depth to obtain first-hand information to understand their cognition and attitude regarding low carbon consumption. In order to explore the main factors that drive the carbon capability of urban residents and establish a policy guidance path, it is necessary to identify the barriers perceived by urban residents related to the implementation of low-carbon behavior.
In previous qualitative studies, face-to-face interviews have often been used to obtain the required information. In this study, in addition to the usual face-to-face interviews, we used the QQ chat platform WeChat chat platform to conduct interviews. QQ chat, which is short for Tencent QQ, is an internet-based instant messaging software. At present, QQ is available for Microsoft Windows, OS X, Android, iOS, Windows Phone, and other mainstream platforms. QQ supports online chat, video calls, point-to-point breakpoint file continuation, shared files, network hard disk, custom panel, QQ mailbox, and other functions, and it can be connected to a variety of communication terminals. WeChat is also a free messaging service for smart terminals. WeChat supports voice messages, video, images, and text messages, which can be sent free of charge (where a small amount of the network traffic is consumed) over the network across communication operators and across operating system platforms. In this study, voice call, video call, and messaging platforms were used for interviews. Participants were free to choose their preferred platform for the interviews.
This type of online interview has the following advantages: the interviewees do not have to meet with the interviewers directly, which is more convenient in terms of time and space; the interviewees do not feel constrained and they may answer more freely and truthfully; the conversation is not easily influenced by the verbal and behavioral language of the interviewer; and the answers can be more considered and logical. Therefore, we conducted in depth, one-to-one interviews via the QQ and WeChat chat platforms online. In the interviews, we used a method based on questions in a focused interview, where the interviewer set up a participatory dialogue and guided the interviewees to focus on a specific subject from their own point of view. Each in-depth interview lasted about 1 h and sufficient time was allowed for reflection by the interviewees. Before the formal interview, the interviewer first explained the subject and the issues considered with the interviewee via the message platform. The interview was based on the principles of openness, interaction, and confidentiality. According to the requirements of grounded theory, the interviews involved no presuppositions and paradigms, but simple interview outlines were specified in advance (see Table 1) to improve the efficiency of the interviews.
Table 1.
Outline of the open-ended interview.
In the interview, further tracked questions focused on the problems in Table 1 and the concept categories were captured in order to explore the interviewee’s inner psychology as deeply as possible to extend the interview content. For example, when asked what measures the government should implement to promote the carbon capability, if the interviewee mentioned monitoring, then the interviewer asked: “Do you think government supervision can promote carbon enhancement? Can you specify how the government should monitor it?”
3.3. Sample Selection
The interview is the main source of qualitative research data, and thus the conclusions obtained, so the interviewees should be selected carefully. Therefore, the interviewees needed to have some understanding of the carbon capability, and low-carbon related concepts and behaviors. Representative urban residents were identified by combining theoretical sampling with stratified sampling, where the representative residents had some understanding of low-carbon consumption and a certain level of educational knowledge []. We limited the interviewees by age to 20–45 years and they comprised urban residents with undergraduate educational levels or above, as well as having some understanding of low-carbon consumption and behavior []. We also considered gender, age, occupation, and other variables to ensure that a reasonable sample structure was obtained in accordance with the real situation. After theoretical sampling and stratified sampling, two specific interviews were conducted. The sample size was determined based on the principle of theoretical saturation, i.e., sampling until the new samples no longer provided new important information. After 38 subjects had been interviewed, the answers given in the last three interviews assessed by content analysis were unable to add new information to the study, so the content was saturated. According to this process, 35 participants were identified. The data showed that the sample matched the diversity requirements for the qualitative study, including different genders, ages, regions, and occupational backgrounds. The basic information for the interviewees is shown in Table 2.
Table 2.
Statistical information for the interviewees.
4. Category Extraction and Model Construction
After sorting the interview records, two-thirds of the interview records were randomly selected for root coding analysis and other one-third were tested for grounded theoretical saturation. In order to ensure the reliability and validity of the study, the grounded coding program developed by Strauss and Corbin was strictly applied in the grounded coding process []. In addition, in order to avoid the effects of personal prejudice on the coding results and to improve the objectivity and scientific validity of the coding, we combined personal coding and expert consultation in this study.
4.1. Open Coding
In the encoding process, open coding or first-level coding is also known as open login or level 1 login. During the open coding process, we tried to use the original words of the interviewees as much as possible in order to name the concepts directly or to extract the related concepts, thereby eliminating the effects of prejudice by the individual coder as much as possible. We invited five related professional researchers to organize the data from the interviews and collected 1021 expressions related to the “carbon capability of urban residents.” In order to identify the factors that strongly influence the carbon capability of urban residents, we excluded relatively simple and vague answers from the interview records, and we finally obtained more than 800 original sentences and the corresponding initial concepts. The number of initial concepts was high and there was a certain degree of crossover between them, so the initial concepts with a repetition frequency of more than five times were selected for categorization, and individual contradictory initial concepts were also eliminated at the same time. Open coding commenced after the first interview. In the first interview, some concepts were sorted and the correlations and differences between these concepts were analyzed to yield some final categories. Next, the second interview was conducted by targeting the problems found in the coding process and the sorting of the concept categories. It should be noted that not everyone was interviewed twice. After the first interview, we open coded the collected data. If questions or doubts remained regarding some of the participants, we contacted them to arrange a second interview. This process was required because the numbers of concepts and categories determined by coding were relatively high, and the related concepts and categories were repeated in the coding process, so the interview could not proceed and coding could not reach the next level. Table 3 presents the conceptualization and categorization processes based on the original interview records. The categorization results comprised factors related to the carbon capability of urban residents. Considering limitations on space for this article, we only list representative primitive record statements and the initial concepts for each category.
Table 3.
Process and results of open coding.
4.2. Axial Coding
In the encoding process, axial coding or secondary encoding is also known as associative login or axis login. Axial coding is a key component of grounded theory analysis. The original codes for the objects or concepts generated in the open encoding process are the major focus of the analysis in axial coding. Axial coding follows a coding paradigm comprising: “reason-phenomenon scene-mediation conditions-action/interaction strategy-results” []. This paradigm combines every concept identified in the open coding process to form a main category, as well as developing and testing the relationship among the concepts. It should be noted that the use of an analysis “paradigm” is important because it provides a perspective for viewing the original concept and a heuristic analysis tool to help organize the systematic decentralization of the original concept.
Axial coding involves the discovery and establishment of various relationships between conceptual categories. In axial coding, researchers only analyze one category at a time by exploring the correlations with this category and analyzing potential correlations between each category at the conceptual level. Therefore, this process is called the “axis” or “spindle.” After analyzing the correlations between each group of categories, we need to recognize the level of the category in the group, i.e., the main category and sub-category, before establishing the relationships between the principal category and sub-categories by continual comparative analysis. The main category identification process (axial coding process) is shown in Table 4.
Table 4.
Process and results of axial coding.
4.3. Selective Coding
In the coding process, selective coding or three-level coding is also known as core login or selective login. Selective coding is based on applying spindle coding to further identify and systematically analyze the relationships between categories and categories. Selective coding is a form of systematic analysis for identifying the core category from the main category and systematically establishing the connections between the core category and other categories. In the continual comparative analysis process, the core category must be repeatedly identified as dominant in most categories and it should clearly describe the relationships between most categories. Most categories can be included in a theoretical framework with good coverage. After in-depth mining, the typical relationships between the main categories determined by selective encoding are shown in Table 5.
Table 5.
Selective coding results.
4.4. Saturation Test
Theoretical saturation testing refers to the further development of a category feature based on the use of no additional data as the criterion for stopping sampling []. After sorting the interview records, two-thirds of the interview records were randomly selected for root coding analysis and one-third were tested for grounded theoretical saturation. The coding analysis of the remaining one-third of the interview records was consistent with the above description, where we conducted open coding, axial coding, and selective coding. Information saturation was determined by continuous comparative analysis. The saturation test was complete and the qualitative analysis ended when no new conceptual categories could be found. In this study, the results showed that the categories in the model were sufficiently developed, and no new categories or relationships were found for the main carbon capability categories of urban residents and no new constituent factors were formed within the main categories. Therefore, we consider that the analysis performed in this study was theoretically saturated.
4.5. Model Construction
Based on the analysis described above, we identified the core drivers of the carbon capability in urban residents and analyzed their interactions. The specific driving factors comprised the individual factors, organizational factors, social demographic variables, utility experience perception, policy situation, low carbon choice cost, and technological situation. In addition, based on the typical relationship structure (Section 4.3), we determined the core category for the multi-layer factors that drive the carbon capability of urban residents and the policy guidance path. We then developed a new theoretical framework comprising the factors that drive the carbon capability in a theoretical model of the mechanisms that drive the carbon capability of urban residents, as shown in Figure 2.
Figure 2.
Comprehensive theoretical model of the mechanisms that drive the carbon capability of urban residents.
5. Discussion
According to the variables (individual factors, organizational factors, and social factors) that affect the carbon capability, we identified two key drivers based on the in-depth interviews: ecological personality and social currency. These two factors have been considered little in previous studies. (1) Ecological personality. Based on the in-depth interviews with residents and experts, we found that the personality traits of residents can affect the construction and development of their carbon capability, and the acceptance of the ecological environment concept can actually promote the implementation of low-carbon consumption behavior. According to previous studies, personality traits will affect the implementation of individual low-carbon consumption behavior. The ecological and environmental consequences of changes in consumption patterns by ordinary consumers are ultimately limited. We cannot be overly optimistic until the current consumption pattern changes because the deterioration of the ecological environment will continue [,,]. In particular, the ecological personality is not a traditional psychological personality, but instead it can be regarded as an ecological trait. Thus, from the perspective of an ecological civilization, the traditional personality connotation can no longer fully explain individual behavioral changes in an ecological situation, and the specific connotation of personality is changing constantly due to the change from an industrial civilization to an ecological civilization. Therefore, the ecological personality trend is evolving into a necessity []. The ecological personality combines a unique and stable thinking mode, and behavioral style based on the ecological concept and the fusion of the human social mentality and natural ecology [], which have important effects on the construction and promotion of the carbon capability. (2) Social currency. This factor conforms with Bandura’s social learning theory. According to Bandura’s social learning theory, human behavior is the result of information processing activities and their interactions with internal factors and environmental factors []. Thus, low carbon consumption behavior is a consequence of individual personality, psychological consciousness, and external social factors. In our daily lives, we share various types of information with friends, such as via Weibo (this “MicroBlog” is a social network platform in China for share briefs and real-time messages via an attention mechanism), and the circle of friends allows others to express themselves. If people receive a message that attracts attention and conveys their likes and dislikes regarding low-carbon behavior, then the likelihood of choosing and implementing low-carbon consumption will be greatly increased [,]. A message that makes someone feel unique is a form of social currency. Social currency is derived from the concept of social media economics, which measures the tendency of users to share brand-related content. In a study of “content sharing” via Internet social networking, Magdol and Bessel concluded that when people communicate with others, they are not only trying to communicate information because “people also want to spread certain information about themselves” []. Thus, people subconsciously want to “label” themselves by talking to others about what they see as their ideal self, which can be funny, intelligent, strong, beautiful, or rich. Our in-depth interviews demonstrated that social currency is factor that can drive the carbon capability of urban residents.
There is a bidirectional interaction between utility experience perception and carbon capability of urban residents. Utility experience perception is a decisive factor that affects the development of the carbon capability. Thus, when the individual’s perception of the outcome of a certain capability tends to be negative, then they consider that the capability does not have any benefit for them, so there is no possibility of carbon capability construction and development. Very few studies have analyzed the impact of utility experience perception on the carbon capability. The meaning of utility experience perception and its relationship with the carbon capability of urban residents was defined mainly according to the results of the in-depth interviews. According to the contents of the interviews, most residents suggested that low-carbon behaviors can reduce economic expenses, bring spiritual satisfaction, protect the environment, and obtain other outcomes. Therefore, we defined the low-carbon consumption behavior as a carrier of the carbon capability, which can lead to utility experience perception, and affect the construction and development of the carbon capability of urban residents. This effect can be positively promoted or reversed, and thus there is a bidirectional interaction between utility experience perception and the carbon capability of urban residents.
Similar to the “attitude behavior” gap, there is a significant gap between utility experience perception and the carbon capability of urban residents. If an individual has a positive utility experience perception, the carbon capability does not necessarily increase. In the interviews, we obtained some data that supported the perception of the utility experience and the generation of the carbon capability in a similar manner to the relationship between behavioral will and behavior. Few studies have investigated the relationships between environmental attitudes (will/intention) and environmental behavior, but most showed that pro-environmental attitudes lead to environmentally friendly behavior []. Some studies found incomplete agreement between environmental attitudes (will/intention) and environmental behavior, but they demonstrated a synergy between environmental attitudes (will/intention) and environmental behavior. For example, a study of the energy use attitude and actual energy use behavior of residents in three regions of Finland found a gap between the two []. The energy use attitude of the residents tended to favor low-carbon or green behaviors, but other factors that affected the comfort of life meant that the actual rate of change in behavior was very slow []. Thus, similar to the gap between “attitude and behavior,” we found a clear gap between the construction of the carbon capability of urban residents and the perception of development and the utility experience, which requires further study.
The low carbon selection cost is an internal situational factor related to the carbon capability of urban residents and by acting as an internal regulatory variable, it exerts a regulatory effect between utility experience perception and the carbon capability. The in-depth interviews showed that many urban residents have not implemented low-carbon behavior, mainly because they feel that low-carbon products are more expensive and they find them inconvenient. If the implementation of a specific low-carbon consumption behavior is very difficult and it causes discomfort in one’s everyday life, as well as requiring more time and effort, then the possibility of its implementation will be very low, which may counteract the perceived positive utility experience that has been generated. Therefore, the low carbon selection cost acts as an internal regulatory variable with a regulatory effect between utility experience perception and the carbon capability. The individual will evaluate the costs and benefits of an individual behavioral choice before making a decision, and the individual will reject the choice when the cost exceeds a certain level. The cost for an individual choosing a low-carbon behavior includes the cost of selecting and implementing low-carbon consumption behavior, but also the costs of transforming traditional consumption habits and implementing a behavioral choice. These internal situational factors influence the implementation of low-carbon consumption patterns.
The technological situation and the policy situation are external situational factors that affect the carbon capability of urban residents, and as external regulatory variables, they have regulatory interactive effects between the utility experience perception and the carbon capability. According to behavioral theory, attitudes regarding individual environmental awareness, purchasing, and consumption behavior will be affected by the product price, performance, and convenience []. Therefore, when individuals make a low-carbon consumption decision, their behavior will be affected by the price, performance, and convenience of the product. More comprehensive considerations of low-carbon products should consider their technological maturity, availability, convenience, and other effects. In addition, the degree of policy intervention, validity, and infrastructure improvement also influence individual low-carbon lifestyle choices to a great extent []. According to the in-depth interviews, many urban residents do not use low-carbon travel modes because the infrastructure is not adequate and many other studies reached a similar conclusion [,]. Therefore, adequate infrastructure is an important requirement for low-carbon behavior. Moreover, the government should improve the relevant system policies and increase policy support. Based on the results of the in-depth interviews, we identified technological situational factors and policy situational factors as external situational factors that affect the carbon capability of urban residents, such as the technological maturity of products, accessibility, and infrastructure completeness. We also found a regulatory interaction between utility experience perception and the carbon capability.
6. Conclusions and Policy Implications
Based on the grounded theory, we showed that individual factors, organizational factors, social factors, utility experience perception, policy situation, low carbon selection cost, technical situation, and social demographic variables are the main factors that drive the carbon capability of urban residents. The individual factors mainly include the ecological personality and comfort preference. The organizational factors include organizational values, organizational system norms, and low carbon atmosphere. The social factors mainly include social consumption culture, social norms, and social currency. The policy situational factors mainly include the degree of policy popularization and the validity of policy implementation. The cost of low carbon selection mainly includes personal economic cost, habit transformation cost, and behavior implementation cost. The technological situational factors mainly include product technological maturity, product availability, and infrastructure completeness. The social demographic variables include individual statistical characteristics, family statistical characteristics, organizational statistical characteristics, and urban statistical characteristics.
The theoretical contributions of this study are as follows. (1) We systematically explored the driving factors that affect the urban carbon capability and identified the leading factors related to the carbon capability (individual factors, organizational factors, and social factors), the perception of utility experience, internal situational factors (low carbon selection cost), and external situational factors (policy situation and technical context). (2) Based on this multi-layer exploration of the factors that influence the individual, organization, and society, we constructed a theoretical model of the factors that drive the carbon capability of urban residents, including the mechanism responsible for forming the carbon capability of urban residents, and we suggested that the perception of utility experience is an important individual factor. Organizational factors and social factors are the three main variables that influence the carbon capability, which is regulated by situational factors. The perception of utility can affect the generation and development of the carbon capability, but it can also have the reverse effect on the carbon capability. (3) The multi-layer driving factors identified in this study contribute greatly to carbon capability research. The ecological personality among the individual factors and social currency among the social factors have rarely been investigated in previous studies.
The conclusions of this study are also important for management practice. In order to effectively guide the development of the carbon capability of urban residents and implement low-carbon behavior, the three aspects shown in Figure 3 should be considered when formulating guidance policies.
Figure 3.
“Advanced cycle” for the construction of the carbon capability of urban residents, with positive utility experience perception as the core.
(1) The integrated construction of a strategy for increasing the carbon capability at the levels of the individual, organization, and society. At the social level, the government should build a positive consumer culture and guide positive social norms. At the organizational level, it is necessary to build the organizational carbon value, create a low-carbon attitude in organizations, and establish low-carbon system norms. At the individual level, the government should build a positive ecological personality and cultivate ecological citizens, as well as improving low-carbon security and guiding rational and comfortable preferences. In order to achieve consistent effects on the individual, organization, and society in the terms of the cultural atmosphere, institutional norms, ecological personality, value orientation, and rational preferences, we need to address the following issues. (1) Governmental aspects such as improving appropriate laws, regulations, and standards of environmental protection, establishing the concept of unified economic development and environmental protection, promoting balanced development, providing ecological education to all people, cultivating ecological citizens, improving the system for environmental information disclosure, enhancing the supervision system, and implementing “carbon-free” operations. (2) Actively encourage low-carbon behavior by enterprises, such as promoting a low-carbon management model, establishing low-carbon guidance system norms, maximizing environmental benefits, improving the technological level of low-carbon products and services, and reducing direct/indirect carbon emissions as much as possible while still satisfying the requirements in terms of comfort for residents. (3) Positively promoting a low-carbon lifestyle among the public, such as encouraging a green diet, green clothing, green living, green travel, and building a low-carbon community.
(2) Strategies for enhancing the carbon capability based on positive utility experience perception. The carbon capability has a positive influence on utility experience perception, and utility experience perception has a positive effect on the carbon capability, so positively and efficiently enhancing the carbon capability will further enhance and consolidate the carbon capability of urban residents. The government can motivate urban residents by rewarding innovative low-carbon applications, subsidizing low carbon products, and rewarding advanced low-carbon individuals/enterprises in order to stimulate urban residents and help urban residents to build their own carbon capability. The government should spread information to the public about how climate warming is caused by high carbon emissions as well as its impacts on physical and mental health, thereby enhancing the perception of the public. The government should improve the purchase channels and provide guidelines for low-carbon products to ensure that urban residents have positive economic experiences when selecting low-carbon products, thereby enhancing their economic perception of these products. For example, on the consumer side, subsidies should be provided for goods such as energy-saving lamps and new energy automobiles, and the low-carbon preferences of urban residents must be cultivated. Furthermore, by growing the economy, environmental protection, value, and active experiences related to low carbon, we can increase the positive cognition of the carbon capability among residents and help them to build and enhance their own carbon capability.
(3) Situational factors have significant effects on promoting the utility-related perception of the carbon capability. Positive intervention strategies related to situational factors are required, such as improving economic policies to promote energy conservation and reduce emissions, as well as considering the popularization and implementation of policies. First, the government should innovate methods for popularizing low carbon knowledge and technology by explaining the specific regulations and implementation rules for policies to residents in various forms, and by implementing low-carbon guidance policies that are closely related to the interests of residents. Second, these strategies may include improving the energy saving and emissions reduction investment mechanism and reducing the costs of low carbon selection, improving the maturity of low-carbon technology, implementing low-carbon product projects and improving the low carbon product purchase channel, and constructing adequate infrastructure and increasing its effective supply. In particular, it is necessary to establish unified green product classification standards, certification bodies, and maturity marking systems. In addition, in terms of the infrastructure supply, the government should try to improve the modernization of the infrastructure, promote regional infrastructure development, and accelerate the development of infrastructure with a green low carbon cycle, as well as conducting regular maintenance and upgrading to ensure that the basic living needs of residents are met.
Author Contributions
Conceptualization, J.W. and H.C.; Methodology, J.W.; Validation, H.C. and R.L.; Formal Analysis, J.W.; Investigation, J.W.; Resources, J.W., H.C. and R.L.; Writing-Original Draft Preparation, J.W.; Writing-Review & Editing, J.W. and H.C.; Visualization, J.W. and H.C.; Supervision, H.C. and R.L.; Project Administration, J.W. and H.C.; Funding Acquisition, J.W., H.C. and R.L.
Funding
This research was funded by [National Natural Science Funding of China] grant number [71473248, 71673271, 71473247, and 71273258], [Major project of National Social Science Funding of China] grant number [16ZDA056], [Jiangsu Philosophy and Social Sciences Excellent Innovation Cultivation Team] grant number [2017ZSTD031], [333 High-level Talents Project of Jiangsu Province] grant number [2016], [Teaching Education Reform and Practice of Jiangsu Province] grant number [JGZZ16_078], [Innovation Team Program of the China University of Mining and Technology] grant number [2015ZY003], [Social Science Foundation of Jiangsu Province Project] grant number [14JD026], [“13th Five Year” Brand Discipline Construction Funding Project of China University of Mining and Technology] grant number [2017], [China Postdoctoral Science Foundation] grant number [2017M620459 and 2018T111080], [Think Tank of Green Safety Management and Policy Science (2018 "Double First-Class" Initiative Project for Cultural Evolution and Creation of CUMT)] grant number [2018WHCC03].
Conflicts of Interest
The authors declare no conflict of interest.
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