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ORIGINAL RESEARCH article

Front. Psychol., 26 October 2022
Sec. Environmental Psychology
This article is part of the Research Topic Understanding Sustainable Energy Transition Pathways: A Social Science Approach View all 9 articles

Demographic differences in public acceptance of waste-to-energy incinerators in China: High perceived stress group vs. low perceived stress group

Jiabin ChenJiabin Chen1Xinyao HeXinyao He1Ye ShenYe Shen1Yiwei ZhaoYiwei Zhao1Caiyun CuiCaiyun Cui2Yong Liu
Yong Liu1*
  • 1School of Civil Engineering and Architecture, Zhejiang Sci-Tech University, Hangzhou, China
  • 2School of Civil Engineering and Architecture, North China Institute of Science and Technology, Langfang, China

Demographic characteristics have been recognized as an important factor affecting public acceptance of waste-to-energy (WTE) incineration facilities. The present study explores whether the differences in public acceptance of WTE incineration facilities caused by demographic characteristics are consistent in residential groups under different perceived stress using data collected by a large-scale questionnaire survey (1,066 samples) conducted in three second-tier cities in China. The result of data analysis using a T-test (one-way ANOVA) shows firstly that people with low perceived stress have higher public acceptance of WTE incineration facilities. Second, the differences in public acceptance of WTE incineration facilities caused by demographic characteristics (gender, educational attainment, and age) vary in residential groups with different perceived stress levels. The findings enrich the knowledge system related to demographic characteristics research on NIMBY infrastructure projects and provide the theoretical basis for the government to formulate more targeted policies about NIMBY infrastructure sitting.

Introduction

The global annual output of municipal solid waste has reached 1.3 billion tons, and it is expected to reach 2.2 billion tons/year in 2025, with an increase of 70% (Fang and Li, 2019). With the rapid increase of municipal solid waste, more and more attention has been paid to the issue of how to treat municipal solid waste more efficiently and environmentally (Kalyani and Pandey, 2014). Compared with the current mainstream landfill treatment, WTE incineration provides a more reasonable solution for the field of municipal solid waste disposal. Specifically, WTE incineration can effectively reduce the volume of solid waste, thus protecting land resources and realizing sustainable development of clean energy utilization (Dudley, 2018). Therefore, whether from the point of view of ecological environment protection or energy utilization, WTE incineration is considered to be the best option for solid waste treatment (Ogunjuyigbe et al., 2017).

However, with the popularization of WTE incineration facilities, a “double paradox” appears in the field of garbage disposal. Although the public knows its important role in the process of sustainable waste treatment, the negative impact of WTE incineration facilities makes the residents near the facilities very excluded (Zhang et al., 2015). This social phenomenon that residents oppose the development of “potentially hazardous facilities” in the local area is also called the NIMBY (Not In My Backyard) effect (Schively, 2007). NIMBY conflicts have not only caused great trouble to the government in urban safety management but also caused great economic losses (Song et al., 2017). Therefore, the siting of WTE incineration facilities is not only a technical challenge but also a complex combination of social, economic, environmental, and technical problems (Mah et al., 2014).

Previous studies have focused on the public acceptance of WTE incineration projects to measure the public response to the facilities (Gunter and Harris, 1998). As an important individual feature, demographic characteristics are considered to be closely related to public acceptance (Flynn et al., 1994). However, research on this issue is currently insufficient. First, although demographic characteristics such as gender, educational attainment, age, race, income level have been proved to affect public acceptance directly (Kahan et al., 2007; Wang and Kim, 2019), some studies have shown that the demographic characteristics of residents living in high-stress communities near potentially hazardous facilities have no significant impact on public acceptance (Yang et al., 2006; Weiner et al., 2013). Second, previous research on the influence of demographic characteristics on public acceptance mainly has focused on residents living in high-stress communities near potentially hazardous facilities (Gustafsod, 1998), with research targeting laypeople (those living further away), an important public opinion base group in the process of building potentially hazardous facilities, mostly lacking. Third, whether the difference of public acceptance of WTE incineration facilities caused by demographic characteristics is consistent in residential groups under different perceived stress has not been fully demonstrated.

To fill the above knowledge gap, the current study attempts to explore the relationship between demographic characteristics and public acceptance in different perceived stress groups using data collected by a large-scale questionnaire survey (1,066 samples) conducted in three second-tier cities in China. The findings enrich the knowledge system related to demographic characteristics research on public acceptance and provide the theoretical basis for the government to formulate more targeted policies about NIMBY infrastructure sitting.

Literature review

Public acceptance and demographic characteristics

Public acceptance is often used to measure the public’s general attitude towards new technologies and express their willingness to accept new technologies (Sun and Zhu, 2014). Du and Zhu (2019) divide the factors influencing public acceptance of potentially hazardous facilities into two categories: personal factors and institutional environment factors. On the one hand, institutional and environmental factors, such as public participation and information disclosure, have been proved to have a direct impact on public acceptance (He et al., 2013; Wu, 2017). On the other hand, individual factors such as demographic factors (gender, age, educational attainment, etc.) and social-psychological state (perceived risks, perceived fairness, perceived benefits, etc.) have also been verified in previous studies (Kikuchi and Gerardo, 2009; Besley, 2010; Roh and Kim, 2017).

To carry out this research better, this paper summarizes the influence of demographic characteristics on public acceptance of potentially hazardous facilities. Demographic characteristics that affect public acceptance include gender, age, race, educational attainment, income level, distance from potentially hazardous facilities, and so on. A substantial body of studies showed that white, well-educated, high-income, males and people living far away from facilities have higher public acceptance (Wang and Kim, 2019). First, white male is considered to have higher rights, status, and social trust, so their attitudes and views on new technologies and potentially hazardous facilities are different from others (Kahan et al., 2007). The typical “white male” effect holds that white males not only have much less perceived risks than others but also have greater perceived benefits than others, which makes them more likely to accept potentially hazardous facilities (Flynn et al., 1994). In another survey across the United States, Britain, and Switzerland, it was concluded that the different attitudes of gender towards nuclear energy were interpreted as different roles of gender in risk perception: females pay more attention to nuclear energy and worry about its negative benefits, while male mostly regards this issue as a scientific and technological issue (Rabow et al., 1990). Secondly, the number of people who support the construction of potentially hazardous facilities increases with age, because with the increased age, the elder is more aware of the help of facilities to the local economy (Greenberg and Truelove, 2011). Moreover, the elderly realizes the importance of more energy regeneration and new energy transition, so they have become staunch supporters of the construction of nuclear and renewable energy facilities (Greenberg, 2009). Thirdly, scholars from different countries have proved that when respondents have better educational backgrounds, they are more likely to have a clear understanding of the benefits of potentially hazardous facilities and are more willing to accept potentially hazardous facilities (Choi et al., 2000; Stoutenborough et al., 2013; Sun and Zhu, 2014). Finally, in the study of the distance of hazardous facilities in the residential area, the residents living near the nuclear power plant and ordinary people have completely different views on nuclear power plant facilities, because the closer they live, the more intuitively they can feel the risks brought by the potentially hazardous facilities, and the more they are excluded from building such facilities near their residential areas, which is a typical “NIMBY “effect (Van der Horst, 2007).

Perceived stress

Lazarus (1966), a well-known psychologist, put forward the concept of psychological stress. Psychological stress refers to a subjective psychological feeling produced by individuals when they realize that the requirements of the internal and external environment threaten them or exceed their coping ability. The study of stressors usually includes two aspects. On the one hand, Holmes and Rahe (1967) concluded the source of individual’s psychological stress as the major events in life, which lead to the loss of internal balance of the body and prompt individuals to make new self-adjustments. On the other hand, Lazarus and Folkman (1984) summarized that the source of psychological stress is not major life events but small annoyances in daily life. The constant accumulation of these annoyances consumes people’s energy and physical strength and ultimately harms their health.

Stress is closely related to the physical and mental health of individuals (Lupien et al., 2009). Moderate stress can improve personal health and the ability to adapt to social life. However, too strong and persistent stress hurts physical and mental health, affecting people’s perception and social behavior (Pengilly and Dowd, 2000). According to the theory of self-defense mechanism, when faced with stress, the human body’s coping is an unconscious psychological defense mechanism, and individuals will unconsciously use defense mechanisms such as denial, evasion, and projection to deal with problems (Freud, 2018). Therefore, there are significant differences between individual perception and social behavior in stress groups and non-stress groups, which have also been verified by many experiments.

First, perceived stress enhances the perceived risk of individuals. The results of an experiment on stress and perceived risk of rescue workers show that rescue workers face the risk of injury repeatedly during work, and this psychological stress makes the risk perception of rescue workers higher than that of ordinary people (Schneider and Bengel, 2014). Besides, the same conclusion is also reflected in the experiment on risk-taking. Nowacki et al. (2019) indicated that compared with people without stress, people with psychosocial stress are less willing to take risks when they face new decisions. Second, high perceived stress reduces one’s trust in others. Potts et al. (2019) pointed out in an experiment to explore the relationship between acute stress and prosocial decision-making that acute stress reduces the tendency of personal trust and changes people’s decision-making behavior. Finally, the high perceived stress affects residents’ perceived fairness. This conclusion was confirmed in an experiment about organizational fairness because researchers found that long-term stress brings about health problems such as inflammation, which also affected individuals’ perception of fairness (Elovainio et al., 2010).

Perceived stress, demographic characteristics, and public acceptance

Under different conditions of perceived stress, the differences in public acceptance of WTE incineration facilities caused by demographic characteristics are consistent different. First, although women’s acceptance of potentially hazardous facilities is significantly lower than that of men because of their higher risk perception, the conclusion has been verified (Flynn et al., 1994; Gustafsod, 1998). However, Weiner et al. (2013) concluded in a survey on tolerance of environmental risks. In the general public, men’s tolerance for the environmental risks of potentially hazardous facilities is higher than that of women. However, in communities with high environmental stress, the gender gap in risk tolerance no longer exists, because men and women have the same resistance when facing threats from the environment for a long time. In addition, according to Liu et al. (2018) survey on the public acceptance of WTE projects by residents living near WTE facilities, the results also show that gender differences do not lead to significant differences in public acceptance, because all residents living in WTE incineration plants are subjected to environmental stress from facilities, resulting in consistently low public acceptance.

Secondly, the educational background may change one’s cognitive level to a certain extent, so the educational background is also an important factor affecting the public’s acceptance of potentially hazardous facilities (Choi et al., 2000). Sun and Zhu (2014) found that public with higher education level have higher acceptance of nuclear energy, because they know more about nuclear energy. However, according to Yang et al. (2006), public who also live in communities with high environmental stress (near nuclear power plants) in China shows that, contrary to previous conclusions, the higher education levels, the lower acceptance. This is largely because of that people with higher education are more concerned about their living environment and health, thus overestimating the risk of nuclear power.

Therefore, throughout past research results, perceived stress can influence individuals’ acceptance of potentially hazardous facilities, and this may lead to changes in the influence of demographic characteristics on public acceptance. For the general public, male, with highly education will have higher public acceptance of potentially hazardous facilities. For groups with high perceived stress, the difference in public acceptance caused by individual demographic characteristics will change. However, previous studies mainly focused on local community residents living around potentially hazardous facilities (Greenberg and Schneider, 1995; Weiner et al., 2013), the research on the influence of perceived stress on public’s acceptance of laymen (those who live far away and have nothing to do with the industry) is mostly lacking.

Research design

Overall research framework

On the basis of emphasizing the differences in public acceptance caused by demographic characteristics, the study focuses on laypeople and explores whether gender, age, educational attainment, and income still have a significant difference on public acceptance under different perceived stress groups sample.

Figure 1 shows the research framework of empirical research in the study. First, according to the literature review, the study designs a questionnaire that included three parts: demographic information, perceived stress level test, and the test of WTE incineration acceptance. Second, a large-scale questionnaire survey was conducted in one city in East China, Central China, and South China. All the collected samples were divided into high perceived stress group samples and low perceived stress group samples according to the scores of the perceived stress level test. Third, T-test and one-way ANOVA were used to test the three groups of samples, respectively, to explore whether the differences in public acceptance of WTE incineration facilities caused by demographic characteristics are consistent in residential groups under different perceived stress.

FIGURE 1
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Figure 1. Research framework.

Questionnaire design

The research questionnaire consists of three parts. The first part is a survey of demographic information, such as gender, age, and education attainment. According to China’s classification of educational attainment, educational attainment can be divided into two dimensions: Low educated (primary school to high school) and High educated (junior college, undergraduate, postgraduate, and above). According to the standards put forward by the United Nations World Health Organization, the age division can be divided into two dimensions: 18–44 years old (young people), 45 years old, and above (middle-aged and elderly people). The second part is the scale for measuring respondents’ perceived stress. The measurement items are all drawn from the PSS 14 (Perceived Stress Scale 14) proposed by Cohen et al. (1983), which has been tested in the past 30 years, and the results show that it has good reliability and validity and has become one of the most popular stress perception scales in the world. The third part is three measurement items raised by Liu et al. (2018), which related to respondents’ acceptance towards WET incineration projects.

Samples and data collection

Three representative second-tier cities in China, namely Hangzhou (eastern city), Wuhan (central city), and Chongqing (western city), were selected to conduct the survey. The main reasons are as follows: First, cities in different geographical locations have significant differences in cultural and economic characteristics. The survey selected representative cities in each region to satisfy the completeness of the research. Second, these three cities are the centers of the regional economy, with a large population and developed economy, so the demand for WTE incinerators is increasing rapidly. Furthermore, the local governments of these three cities have suffered strong public opposition in the process of introducing potentially hazardous facilities. Therefore, there is urgent to help the local government to improve public acceptance of WTE incinerators by local residents.

The questionnaire survey was conducted from May 13th to May 25th, 2021, in Hangzhou, June 20th to June 30th, 2021, in Wuhan, and August 10th to 15th, 2021 in Chongqing. Local residents living in the selected survey areas were identified as target respondents. Through stratified simple random sampling, 1,200 questionnaires (including 400 in Hangzhou, 400 in Wuhan, and 400 in Chongqing) were sent out to selected respondents. After eliminating the questionnaire with missing items and multiple options, 1,066 valid usable questionnaires were obtained, comprising 335 from Hangzhou (response rate 83.75%), 369 from Wuhan (response rate 92.25%), and 362 from Chongqing (response rate 90.5%).

Table 1 provides the social demographic information of the respondents. Both the gender and age distributions of the respondents are basically consistent with the results of the seventh census in China, which means that the samples collected are representative. Besides, the cities selected in the survey are all economically developed, which makes them have high-quality educational resources. Thus, the distribution of respondents with high educated reached 67.5%, which was higher than the average education level of Chinese residents.

TABLE 1
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Table 1. Demographic characteristics of the respondents.

Data analysis

The analysis of data in the study can be divided into the following two stages. First, descriptive statistics were conducted to evaluate the perceived stress level and public acceptance towards WTE incineration facilities. Second, according to the results of PSS 14 (Perceived Stress Scale 14), people with a total score of 43 or more (with an average score of more than 3 points per question) are considered as people with high perceived stress (Zalaquett and Wood, 1998; Yang and Huang, 2003). Therefore, samples with PSS 14 scores greater than or equal to 43 points are divided into high perceived stress group samples, and samples with PSS 14 scores less than 43 points are divided into low perceived stress group samples. T-test is an appropriate statistical method to detect the differences between two groups of data. For more than two groups of data, ANOVA can be used to detect whether there are differences among three groups (or more) of data (Cui and Churchill, 2003). The purpose of the study is to detect whether the differences in public acceptance caused by demographic differences are consistent among different perceived stress groups. So, the current study adopts T-test and variance as the main methods to explore whether the differences in public acceptance of WTE incineration facilities caused by demographic characteristics are consistent in residential groups under different perceived stress.

Results

Descriptive statistics

Table 2 shows the descriptive statistical results of all variables of the valid questionnaire. The kurtosis coefficients and skewness coefficients of all variables are following a multivariate normal distribution. Therefore, this data is suitable for T-test and one-way ANOVA.

TABLE 2
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Table 2. Statistical results of the descriptive variables.

As shown in descriptive statistics the scores of three terms (F1, F2, and F3) used to express the public’s recognition of WTE incineration facilities are 3.05, 2.77, and 2.54 respectively, which shows that the public acceptance of WTE incineration facilities is low.

Overall sample test

Table 3 shows the results of using T-test and one-way ANOVA to test whether gender, age, education attainment, and income level have a significant difference on public acceptance. In terms of gender, the average score of males for public acceptance terms is 8.829, and that of the female is 7.864. Male’s public recognition of WTE incineration facilities is significantly higher than female’s (p = 0.000). In terms of educational attainment, the average score of the public acceptance items of the group with high educational attainment is 8.501, while that of the group with low educational attainment is 8.072 points. Public acceptance of WTE incineration facilities by the group with higher educational attainment has significantly higher than that of the group with low education (p = 0.018). However, there is no significant difference in the age and income level on public acceptance.

TABLE 3
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Table 3. Test results of the difference of demographic characteristics on public acceptance (overall sample).

In this survey, the overall samples were divided into a high perceived stress group sample (the score of PSS14 was 43–70) and a low perceived stress group sample (the score of PSS14 was 14–42). Among them, there were 283 questionnaires in the high perceived stress group sample (26.55% of the total sample) and 783 questionnaires in the low perceived stress group sample (73.45% of the total sample).

Table 4 explores the difference in public acceptance between high perceived stress group samples and low perceived stress group samples by using a t-test. The average score of the public acceptance terms of the samples in the high perceived stress group is only 5.986, while the average score of the samples in the low perceived stress group is 9.211, with a significant difference (p = 0.000).

TABLE 4
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Table 4. The result of testing the difference in public acceptance among different perceived stress groups.

Group sample test

High perceived stress group sample

Table 5 shows the test results of the T-test and one-way ANOVA in high perceived stress group samples. It can be found that differences in gender, age, educational attainment, and income level have no significant difference on public acceptance.

TABLE 5
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Table 5. Test results of the difference of demographic characteristics on public acceptance. (High perceived stress group samples).

Low perceived stress group sample

Table 6 shows the test results of the T-test and one-way ANOVA in low perceived stress group samples. There are significant differences in public acceptance in terms of gender (p = 0.018); There are significant differences in public acceptance in terms of age (p = 0.032), among which older people have higher public acceptance than younger people. Age has no significant difference on public acceptance.

TABLE 6
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Table 6. Test results of the difference of demographic characteristics on public acceptance. (Low perceived stress group samples).

Discussion and implications

As shown in Table 3, the score of the items used to express public acceptance is only 2.54, 2.77, and 3.05, respectively, which implies that the residents living in second-tier cities in China have a low public acceptance of WTE incineration projects. However, the result is much higher than the score drawn by Liu et al. (2019) and Zhou et al. (2022) using the same questionnaires to investigate local residents near WTE incinerators in Hangzhou and Ningbo, Zhejiang province, and Nanjing, Jiangsu province, with only about 2 points. This result further confirms that residents living near potential hazardous facilities have a more negative attitude towards the facilities (Wang et al., 2019). In addition, Table 4 shows that the public acceptance of the respondents in the low perceived stress group is significantly higher than that in the high perceived stress group (p = 0.000), which proves that perceived stress plays an important role in the public acceptance of WTE projects (Greenberg, 2009). Thus, reducing residents’ perceived stress can be a logical and reasonable measure to deal with the strong public opposition to potentially hazardous facilities. In fact, reducing residents’ perceived stress by introducing and improving the local medical system and improving the local social security system has gradually become one of the popular strategies for local governments to improve public acceptance of potentially hazardous facilities (Wang et al., 2014; Saladino et al., 2020; Simpson et al., 2021).

The results of the overall sample test provide strong empirical support for the difference of demographic characteristics on public acceptance. First, males have higher public acceptance than females, which is consistent with previous studies, such as the research results of Wang and Kim (2019) and Kahan et al. (2007). On the one hand, Karpiak and Baril (2008) hold that females are more eco-centric and pay more attention to the environment than males, so females are more sensitive to the environmental risks brought by potentially hazardous facilities. On the other hand, a key reason for gender differences in public acceptance is related to the different roles of males and females in society. As guardians of health and safety in the family, females are more cautious and easier to learn from the disasters and deaths caused by past technical failures. Males are more willing to discuss the risks and economic benefits of facilities from the technical point of view, which leads females to reject potentially hazardous facilities more than males (Freudenburg and Davidson, 2007; Miller, 2012). Second, people with higher education are more likely to accept WTE incineration facilities than people with low education. Educational attainment may cause individual differences in obtaining information and resources, thus affecting people’s views on technological risks, and indirectly affecting the acceptability of technology (Duan, 2010). Moreover, with the improvement of the educational attainment of individuals, people can feel the importance of facilities, that is, the positive benefits brought by potentially hazardous facilities, whether it is the solution of environmental problems or the promotion of the local economy (Choi et al., 2000; Mitchell et al., 2007). Therefore, bridging the gap in residents’ knowledge about potential hazardous facilities can be an important measure to promote public acceptance of WTE incineration facilities (Sun and Zhu, 2014). When the government increases residents’ awareness of potentially hazardous facilities through timely risk communication meetings and hearings, residents can reduce perceived risks and improve perceived benefits (Chung and Kim, 2009; Ferry and Eckersley, 2015).

In particular, the test results from the high perceived stress groups samples do not support the difference of gender on public acceptance as indicated by the overall samples. This phenomenon may be associated with physical stress responses. On the one hand, according to Traczyk et al. (2015), under the state of high perceived stress, both males and females can easily produce the risk images of past serious accidents, which leads to higher risk perception. Because the negative information such as air pollution caused by WTE incineration facilities makes people who feel high stress bring more risk perception, which makes their public acceptance close and low (Kozyreva et al., 2020). Thus, the finding of the high perceived stress group sample is contrary to the result of the overall sample may be first due to higher risk perception caused by perceived stress. On the other hand, studies from the medical field show that when the individual perceives excessive stress, it will lead to negative abnormal physiological reactions and these reactions often lead to psychological abnormalities such as anxiety, tension, depression, fear, decreased personal efficacy and behavioral disorders such as behavior withdrawal and aggressive behavior increase (Cannon, 1939; Lupien et al., 2009). Therefore, in the high perceived stress groups samples in the study, both males and females have similar physiological and psychological reactions when they bear the same high stress, which means males and females may also have a tendency to escape or resist WTE incineration facilities because of the stress reaction, which also reduces the difference of gender on public acceptance (Weiner et al., 2013).

Similarly, the test results of the sample of the high perceived stress group also failed to support the difference of educational attainment on public acceptance of WTE incineration facilities. As emphasized by the cognitive-affective system theory put forward by Mischel and Shoda (1995), when the change of emotion makes the old cognition and the new emotion does not match, it will lead to the change of cognition, thus alleviating the contradiction between cognition and emotion (Schultheiss et al., 2008). Hence, although the cognition brought by excellent educational background can make the public have a certain cognition of potentially hazardous facilities (Stoutenborough et al., 2013), when the negative emotions caused by perceived stress conflict with cognition, people may overturn the limited cognition of potentially hazardous facilities and hold a negative and exclusive attitude towards them. Meanwhile, Skinner and Wellborn (2019) pointed out that under the state of psychological stress, the individual’s response includes not only the intentional response of controlling the danger, acquiring ability and autonomy, but also the individual’s unconscious psychological defense mechanism. In fact, this kind of defense mechanism may make people with higher education want to control potential dangers through their limited knowledge, which makes it easier to overestimate the influence of potentially hazardous facilities, thus leading to resistance (Yang et al., 2006).

In relation to age, no significant difference of age on public acceptance was observed in the overall sample and high perceived stress group sample, but in the low perceived stress group sample, it was reported that older people had higher public acceptance. There may be two reasons for this result. First, young people are faced with family responsibilities of getting married, giving birth and raising children, so they are more worried about the threat posed by WTE incineration facilities to families and young children, and hold a rejection attitude (Huang et al., 2013; Roh and Kim, 2017). Secondly, in the age when middle-aged and elderly people were born, not only did local governments pay insufficient attention to environmental problems but also the way of controlling environmental problems at that time was not effective enough (Zhu et al., 2014; Xie, 2020). Therefore, after going through a worse environment, they can not only realize the pollution problems caused by urban garbage, but also hope to solve these problems through effective solutions, according to that, they can better accept the benefits that WTE incineration facilities bring to their living environment (Greenberg, 2009). However, with the increase in perceived stress, we found that public acceptance of the WTE incineration facilities by the elderly declined obviously, which was the same as that of the young people. The most possible reason for this phenomenon is the different sources of stress. The main reason for the high perceived stress of the elderly is their health problems, which suggests that the elderly with high perceived stress may face more health-related problems than the elderly with low perceived stress (Folkman et al., 1987; Tsai et al., 2015). Therefore, the elderly with high perceived stress may show more demand for health, which will also make the elderly cautious and skeptical about WTE incineration facilities in the current study (Wang et al., 2001).

Conclusion

In light of the important influence of demographic characteristics on public acceptance of WTE incineration facilities, the current study explores whether demographic characteristics have a significant difference on public acceptance in different groups of perceived stress using a questionnaire and T-test (one-way ANOVA). The research results provide favorable empirical supports that the difference of demographic characteristics on public acceptance produces different results when the perceived stress changes through a questionnaire survey conducted among residents of three second-tier cities in China. The results are as follows:

1. The public acceptance of the WTE incineration project in the low perceived stress group is higher than that in the high perceived stress group.

2. In the overall sample, males have higher public acceptance than females; Groups with high education attainment have higher public acceptance than those with low education attainment.

3. The difference of demographic characteristics (gender, educational attainment, and age) on public acceptance of WTE incineration facilities have been changed in different groups of perceived stress levels.

This conclusion not only enriches the relevant knowledge system of environmental psychology and demographic characteristics research in NIMBY infrastructure projects, but also helps to provide theoretical support for the government, enterprises, and relevant NIMBY professionals to make more effective decisions in the future.

However, the current study still has some limitations. First, the public survey only makes choices for representative second-tier cities in China, which has not been poorly verified in different socio-economic environments. In the future, we will conduct large-scale research on the public with other diverse socio-economic backgrounds (such as first-tier cities with developed economies or poor rural areas) to further verify the influence of perceived stress on the public acceptance of NIMBY infrastructure. Secondly, the study only finds that perceived stress has an impact on public acceptance, Whether the unspecified stress (such as environmental stress, health stress, and employment stress) affects the public acceptance is not divided clearly. Therefore, we will also make a more detailed study on stress to confirm which kind of stress plays a major role in influencing public acceptance. Finally, in different perceived stress environments, the difference of age on public acceptance has not been supported by abundant literature. We will also do relevant research and design in the future to find the potential reasons.

Data availability statement

The original contributions presented in the study are included in the article/Supplementary material; further inquiries can be directed to the corresponding author.

Author contributions

JC: writing—original draft, investigation, and formal analysis. XH: writing—original draft and resources. YL: conceptualization, methodology, project administration, and funding acquisition. CC: software, visualization, and data curation. YS: methodology, validation, and supervision. YZ: software, methodology, and validation. All authors contributed to the article and approved the submitted version.

Funding

This work was supported by the National Natural Science Foundation of China (NSFC; grant nos. 72072165, 71672180, and 72001079), the Soft Science Research Program of Zhejiang Province, China (grant no. 2020C35055), and the Research Foundation of Education Bureau of Zhejiang Province, China (Grant No. Y202045460).

Acknowledgments

We would like to thank the survey work implemented by the graduate students from Zhejiang Sci-Tech University.

Conflict of interest

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.

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.2022.948653/full#supplementary-material

References

Besley, J. C. (2010). Public engagement and the impact of fairness perceptions on decision favorability and acceptance. Sci. Commun. 32, 256–280. doi: 10.1177/1075547009358624

CrossRef Full Text | Google Scholar

Cannon, W. B. (1939). The wisdom of the body (2nd ed.). New York: Norton & Co., 198:113.

Google Scholar

Choi, Y. S., Kim, J. S., and Lee, B. W. (2000). Public's perception and judgment on nuclear power. Ann. Nucl. Energy 27, 295–309. doi: 10.1016/S0306-4549(99)00056-0

CrossRef Full Text | Google Scholar

Chung, J. B., and Kim, H. K. (2009). Competition, economic benefits, trust, and risk perception in siting a potentially hazardous facility. Landsc. Urban Plan. 91, 8–16. doi: 10.1016/j.landurbplan.2008.11.005

CrossRef Full Text | Google Scholar

Cohen, S., Kamarck, T., and Mermelstein, R. (1983). A global measure of perceived stress. J. Health Soc. Behav. 24, 385–396. doi: 10.2307/2136404

CrossRef Full Text | Google Scholar

Cui, X., and Churchill, G. A. (2003). Statistical tests for differential expression in cDNA microarray experiments. Genome Biol. 4, 1–10. doi: 10.1186/gb-2003-4-4-210

CrossRef Full Text | Google Scholar

Du, J., and Zhu, X. F. (2019). Literature review on public acceptance of nuclear energy: research outline, theoretical framework, and prospect. Bull. Chin. Acad. Sci. 34, 677–692. doi: 10.16418/j.issn.1000-3045.2019.06.009

CrossRef Full Text | Google Scholar

Duan, H. (2010). The public perspective of carbon capture and storage for CO2 emission reductions in China. Energy Policy 38, 5281–5289. doi: 10.1016/j.enpol.2010.05.040

CrossRef Full Text | Google Scholar

Dudley, B. (2018). BP statistical review of world energy. BP Statistical Rev. 6:00116

Google Scholar

Elovainio, M., Heponiemi, T., Sinervo, T., and Magnavita, N. (2010). Organizational justice and health; review of evidence. G. Ital. Med. Lav. Ergon. 32, B5–B9.

PubMed Abstract | Google Scholar

Fang, D., and Li, K. (2019). An overview of power generation from municipal solid waste incineration plants at home and abroad. Power Generation Techn. 40, 367–376.

Google Scholar

Ferry, L., and Eckersley, P. (2015). Accountability and transparency: a nuanced response to Etzioni. Public Adm. Rev. 75, 11–12. doi: 10.1111/puar.12303

PubMed Abstract | CrossRef Full Text | Google Scholar

Flynn, J., Slovic, P., and Mertz, C. K. (1994). Gender, race, and perception of environmental health risks. Risk Anal. 14, 1101–1108. doi: 10.1111/j.1539-6924.1994.tb00082.x

CrossRef Full Text | Google Scholar

Folkman, S., Lazarus, R. S., Pimley, S., and Novacek, J. (1987). Age differences in stress and coping processes. Psychol. Aging 2, 171–184. doi: 10.1037/0882-7974.2.2.171

CrossRef Full Text | Google Scholar

Freud, A. (2018). The ego and the mechanisms of defence. London: Routledge.

Google Scholar

Freudenburg, W. R., and Davidson, D. J. (2007). Nuclear families and nuclear risks: the effects of gender, geography, and progeny on attitudes toward a nuclear waste facility. Rural. Sociol. 72, 215–243. doi: 10.1526/003601107781170017

CrossRef Full Text | Google Scholar

Greenberg, M. (2009). Energy sources, public policy, and public preferences: analysis of US national and site-specific data. Energy Policy 37, 3242–3249. doi: 10.1016/j.enpol.2009.04.020

CrossRef Full Text | Google Scholar

Greenberg, M. R., and Schneider, D. F. (1995). Gender differences in risk perception: Effects differ in stressed vs. non-stressed environments. Risk Analysis, 15, 503–511.

Google Scholar

Greenberg, M., and Truelove, H. B. (2011). Energy choices and risk beliefs: is it just global warming and fear of a nuclear power plant accident? Risk Analysis: International J. 31, 819–831. doi: 10.1111/j.1539-6924.2010.01535.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Gunter, V. J., and Harris, C. K. (1998). Noisy winter: the DDT controversy in the years before silent spring. Rural. Sociol. 63, 179–198. doi: 10.1111/j.1549-0831.1998.tb00670.x

CrossRef Full Text | Google Scholar

Gustafsod, P. E. (1998). Gender differences in risk perception: theoretical and methodological erspectives. Risk Anal. 18, 805–811. doi: 10.1111/j.1539-6924.1998.tb01123.x

CrossRef Full Text | Google Scholar

He, G., Mol, A. P., Zhang, L., and Lu, Y. (2013). Public participation and trust in nuclear power development in China. Renew. Sust. Energ. Rev. 23, 1–11. doi: 10.1016/j.rser.2013.02.028

CrossRef Full Text | Google Scholar

Holmes, T. H., and Rahe, R. H. (1967). The social readjustment rating scale. J. Psychosom. Res. 11, 213–218. doi: 10.1016/0022-3999(67)90010-4

CrossRef Full Text | Google Scholar

Huang, L., Zhou, Y., Han, Y., Hammitt, J. K., Bi, J., and Liu, Y. (2013). Effect of the Fukushima nuclear accident on the risk perception of residents near a nuclear power plant in China. Proc. Natl. Acad. Sci. 110, 19742–19747. doi: 10.1073/pnas.1313825110

PubMed Abstract | CrossRef Full Text | Google Scholar

Kahan, D. M., Braman, D., Gastil, J., Slovic, P., and Mertz, C. K. (2007). Culture and identity-protective cognition: explaining the white-male effect in risk perception. J. Empir. Leg. Stud. 4, 465–505. doi: 10.1111/j.1740-1461.2007.00097.x

CrossRef Full Text | Google Scholar

Kalyani, K. A., and Pandey, K. K. (2014). Waste to energy status in India: a short review. Renew. Sust. Energ. Rev. 31, 113–120. doi: 10.1016/j.rser.2013.11.020

CrossRef Full Text | Google Scholar

Karpiak, C. P., and Baril, G. L. (2008). Moral reasoning and concern for the environment. J. Environ. Psychol. 28, 203–208. doi: 10.1016/j.jenvp.2007.12.001

CrossRef Full Text | Google Scholar

Kikuchi, R., and Gerardo, R. (2009). More than a decade of conflict between hazardous waste management and public resistance: a case study of NIMBY syndrome in Souselas (Portugal). J. Hazard. Mater. 172, 1681–1685. doi: 10.1016/j.jhazmat.2009.07.062

PubMed Abstract | CrossRef Full Text | Google Scholar

Kozyreva, A., Lewandowsky, S., and Hertwig, R. (2020). Citizens versus the internet: confronting digital challenges with cognitive tools. Psychol. Sci. Public Interest 21, 103–156. doi: 10.1177/1529100620946707

PubMed Abstract | CrossRef Full Text | Google Scholar

Lazarus, R. S. (1966). Psychological stress and the coping process. United States: McGraw-Hill.

Google Scholar

Lazarus, R. S., and Folkman, S. (1984). Stress, appraisal, and coping. Germany: Springer publishing company.

Google Scholar

Liu, Y., Ge, Y., Xia, B., Cui, C., Jiang, X., and Skitmore, M. (2019). Enhancing public acceptance towards waste-to-energy incineration projects: lessons learned from a case study in China. Sustain. Cities Soc. 48:101582. doi: 10.1016/j.scs.2019.101582

CrossRef Full Text | Google Scholar

Liu, Y., Sun, C., Xia, B., Cui, C., and Coffey, V. (2018). Impact of community engagement on public acceptance towards waste-to-energy incineration projects: empirical evidence from China. Waste Manag. 76, 431–442. doi: 10.1016/j.wasman.2018.02.028

PubMed Abstract | CrossRef Full Text | Google Scholar

Lupien, S. J., McEwen, B. S., Gunnar, M. R., and Heim, C. (2009). Effects of stress throughout the lifespan on the brain, behaviour and cognition. Nat. Rev. Neurosci. 10, 434–445. doi: 10.1038/nrn2639

PubMed Abstract | CrossRef Full Text | Google Scholar

Mah, D. N.-Y., Hills, P., and Tao, J. (2014). Risk perception, trust and public engagement in nuclear decision-making in Hong Kong. Energ Policy 73, 368–390. doi: 10.1016/j.enpol.2014.05.019

CrossRef Full Text | Google Scholar

Miller, L. M. (2012). Females and risk: Commercial wastewater injection wells and gendered perceptions of risk. Risk and Social Theory in Environmental Management, CSIRO, 91–104.

Google Scholar

Mischel, W., and Shoda, Y. (1995). A cognitive-affective system theory of personality: reconceptualizing situations, dispositions, dynamics, and invariance in personality structure. Psychol. Rev. 102, 246–268. doi: 10.1037/0033-295X.102.2.246

PubMed Abstract | CrossRef Full Text | Google Scholar

Mitchell, N. J., Herron, K. G., Jenkins-Smith, H. C., and Whitten, G. D. (2007). Elite beliefs, epistemic communities and the Atlantic divide: scientists' nuclear policy preferences in the United States and European Union. Br. J. Polit. Sci. 37, 753–764. doi: 10.1017/S0007123407000403

CrossRef Full Text | Google Scholar

Nowacki, J., Duesenberg, M., Deuter, C. E., Otte, C., and Wingenfeld, K. (2019). Delayed effects of psychosocial stress on risk taking. Stress 22, 446–454. doi: 10.1080/10253890.2019.1593364

PubMed Abstract | CrossRef Full Text | Google Scholar

Ogunjuyigbe, A. S. O., Ayodele, T. R., and Alao, M. A. (2017). Electricity generation from municipal solid waste in some selected cities of Nigeria: an assessment of feasibility, potential and technologies. Renew. Sust. Energ. Rev. 80, 149–162. doi: 10.1016/j.rser.2017.05.177

CrossRef Full Text | Google Scholar

Pengilly, J. W., and Dowd, E. T. (2000). Hardiness and social support as moderators of stress. J. Clin. Psychol. 56, 813–820. doi: 10.1002/(SICI)1097-4679(200006)56:6<813::AID-JCLP10>3.0.CO;2-Q

PubMed Abstract | CrossRef Full Text | Google Scholar

Potts, S. R., McCuddy, W. T., Jayan, D., and Porcelli, A. J. (2019). To trust, or not to trust? Individual differences in physiological reactivity predict trust under acute stress. Psychoneuroendocrinology 100, 75–84. doi: 10.1016/j.psyneuen.2018.09.019

CrossRef Full Text | Google Scholar

Rabow, J., Hernandez, A. C., and Newcomb, M. D. (1990). Nuclear fears and concerns among college students: a cross-national study of attitudes. Polit. Psychol. 11, 681–698. doi: 10.2307/3791478

CrossRef Full Text | Google Scholar

Roh, S., and Kim, D. (2017). Effect of Fukushima accident on public acceptance of nuclear energy (Fukushima accident and nuclear public acceptance). Energy Sources, Part B: Economics, Planning, and Policy 12, 565–569. doi: 10.1080/15567249.2016.1230797

CrossRef Full Text | Google Scholar

Saladino, V., Algeri, D., and Auriemma, V. (2020). The psychological and social impact of Covid-19: new perspectives of well-being. Front. Psychol. 11:577684. doi: 10.3389/fpsyg.2020.577684

PubMed Abstract | CrossRef Full Text | Google Scholar

Schively, C. (2007). Understanding the NIMBY and LULU phenomena: reassessing our knowledge base and informing future research. J. Plan. Lit. 21, 255–266. doi: 10.1177/0885412206295845

CrossRef Full Text | Google Scholar

Schneider, S. S., and Bengel, J. (2014). Psychological stress and risk perception of rescue personnel of the Technisches Hilfswerk. Notfall& Rettungsmedizin 17, 690–696. doi: 10.1007/s10049-014-1916-x

CrossRef Full Text | Google Scholar

Schultheiss, O. C., Liening, S. H., and Schad, D. (2008). The reliability of a picture story exercise measure of implicit motives: estimates of internal consistency, retest reliability, and ipsative stability. J. Res. Pers. 42, 1560–1571. doi: 10.1016/j.jrp.2008.07.008

CrossRef Full Text | Google Scholar

Simpson, J., Albani, V., Bell, Z., Bambra, C., and Brown, H. (2021). Effects of social security policy reforms on mental health and inequalities: a systematic review of observational studies in high-income countries. Soc. Sci. Med. 272:113717. doi: 10.1016/j.socscimed.2021.113717

PubMed Abstract | CrossRef Full Text | Google Scholar

Skinner, E. A., and Wellborn, J. G. (2019). Coping during childhood and adolescence: a motivational perspective. Life-span development and behavior, 91–134. doi: 10.4324/9781315789255-3

CrossRef Full Text | Google Scholar

Song, J., Sun, Y., and Jin, L. (2017). PESTEL analysis of the development of the waste-to-energy incineration industry in China. Renew. Sust. Energ. Rev. 80, 276–289. doi: 10.1016/j.rser.2017.05.066

CrossRef Full Text | Google Scholar

Stoutenborough, J. W., Sturgess, S. G., and Vedlitz, A. (2013). Knowledge, risk, and policy support: public perceptions of nuclear power. Energy Policy 62, 176–184. doi: 10.1016/j.enpol.2013.06.098

CrossRef Full Text | Google Scholar

Sun, C., and Zhu, X. (2014). Evaluating the public perceptions of nuclear power in China: evidence from a contingent valuation survey. Energy Policy 69, 397–405. doi: 10.1016/j.enpol.2014.03.011

CrossRef Full Text | Google Scholar

Traczyk, J., Sobkow, A., and Zaleskiewicz, T. (2015). Affect-laden imagery and risk taking: the mediating role of stress and risk perception. PloS one 10:0122226. doi: 10.1371/journal.pone.0122226

CrossRef Full Text | Google Scholar

Tsai, A. C., Chi, S. H., and Wang, J. Y. (2015). Association of perceived stress with depressive symptoms in older T aiwanese: results of a population-based study. Geriatr Gerontol Int 15, 535–543. doi: 10.1111/ggi.12307

PubMed Abstract | CrossRef Full Text | Google Scholar

Van der Horst, D. (2007). NIMBY or not? Exploring the relevance of location and the politics of voiced opinions in renewable energy siting controversies. Energy Policy 35, 2705–2714. doi: 10.1016/j.enpol.2006.12.012

CrossRef Full Text | Google Scholar

Wang, X., Cai, L., Qian, J., and Peng, J. (2014). Social support moderates stress effects on depression. Int. J. Ment. Heal. Syst. 8, 1–5. doi: 10.1186/1752-4458-8-41

CrossRef Full Text | Google Scholar

Wang, J., and Kim, S. (2019). Searching for new directions for energy policy: testing the cross-effect of risk perception and cyberspace factors on online/offline opposition to nuclear energy in South Korea. Sustain. For. 11:1368. doi: 10.3390/su11051368

CrossRef Full Text | Google Scholar

Wang, Y., Li, H., Zuo, J., and Wang, Z. (2019). Evolution of online public opinions on social impact induced by NIMBY facility. Environ. Impact Assess. Rev. 78:106290. doi: 10.1016/j.eiar.2019.106290

CrossRef Full Text | Google Scholar

Wang, J. J., Snyder, M., and Kaas, M. (2001). Stress, loneliness, and depression in Taiwanese rural community-dwelling elders. Int. J. Nurs. Stud. 38, 339–347. doi: 10.1016/S0020-7489(00)00072-9

PubMed Abstract | CrossRef Full Text | Google Scholar

Weiner, M. D., Mac Kinnon, T. D., and Greenberg, M. R. (2013). Exploring the gender gap and the impact of residential location on environmental risk tolerance. J. Environ. Psychol. 36, 190–201. doi: 10.1016/j.jenvp.2013.07.012

CrossRef Full Text | Google Scholar

Wu, Y. (2017). Public acceptance of constructing coastal/inland nuclear power plants in post-Fukushima China. Energy Policy 101, 484–491. doi: 10.1016/j.enpol.2016.11.008

CrossRef Full Text | Google Scholar

Xie, Z. (2020). China’s historical evolution of environmental protection along with the forty years’ reform and opening up. Environ. Sci. Ecotechnology 1:100001. doi: 10.1016/j.ese.2019.100001

CrossRef Full Text | Google Scholar

Yang, Y. Z., and Huang, H. T. (2003). An epidemiological study on stress among urban residents in social transition period. Chinese J. Epidemiology 24, 760–764.

PubMed Abstract | Google Scholar

Yang, G. Z., Yu, N. L., Han, C. S., Zhuang, J. Y., Fei, X. J., and Xu, L. (2006). Investigation and analysis on Residents' cognition of nuclear radiation risk around Tianwan nuclear power plant. Chinese J. Radiological Health 1, 69–72.

Google Scholar

Zalaquett, C. P., and Wood, R. J. E. (1998). Evaluating stress: A book of resources, Vol. 2. Chengdu, China: Scarecrow Education.

Google Scholar

Zhang, D., Huang, G., Xu, Y., and Gong, Q. (2015). Waste-to-energy in China: key challenges and opportunities. Energies 8, 14182–14196. doi: 10.3390/en81212422

CrossRef Full Text | Google Scholar

Zhou, Q., Xu, M., Liu, Y., Cui, C., Xia, B., Ke, Y., et al. (2022). Exploring the effects of spatial distance on public perception of waste-to-energy incineration projects. Waste Manag. 143, 168–176. doi: 10.1016/j.wasman.2022.02.033

PubMed Abstract | CrossRef Full Text | Google Scholar

Zhu, S., He, C., and Liu, Y. (2014). Going green or going away: environmental regulation, economic geography and firms’ strategies in China’s pollution-intensive industries. Geoforum 55, 53–65. doi: 10.1016/j.geoforum.2014.05.004

CrossRef Full Text | Google Scholar

Keywords: waste-to-energy incineration project, public acceptance, demographic characteristic, perceived stress, China

Citation: Chen J, He X, Shen Y, Zhao Y, Cui C and Liu Y (2022) Demographic differences in public acceptance of waste-to-energy incinerators in China: High perceived stress group vs. low perceived stress group. Front. Psychol. 13:948653. doi: 10.3389/fpsyg.2022.948653

Received: 20 May 2022; Accepted: 10 October 2022;
Published: 26 October 2022.

Edited by:

Muddassar Sarfraz, Putra Malaysia University, Malaysia

Reviewed by:

Mingxiu Zhan, China Jiliang University, China
Xuefan Dong, Beijing University of Technology, China

Copyright © 2022 Chen, He, Shen, Zhao, Cui and Liu. 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: Yong Liu, jhly1007@zstu.edu.cn

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