Exploring public participation process and its differing degrees in influencing risk perception within the petrochemical industry: a scoping review

Abstract

To evaluate perceived risk, it is necessary to understand both the type of risk and the residents’ perceptions. With the rise of information on technology and digital platforms, new avenues have emerged for examining citizens’ risk perception in participatory settings. However, the lack of theoretical and methodological approaches in this area calls for further research. The objective of this article is to fill the existing research gap by conducting a scoping review of published literature that examines risk perception related to the petrochemical industry, specifically focusing on digital platforms and the utilization of participatory processes in assessing risk perception within this industry context. The review analyzes the types of questions and responses encountered during participatory processes. The authors selected and studied 10 papers in-depth after applying specific selection criteria. They identified two types of risks—natural and technological—associated with the petrochemical industry, and two types of questions: general questions such as demographics, education, and employment, and specific questions such as risk perception, trust in government and company information, type of risk, or proximity to polluted areas. The paper identifies two question types in participatory processes: general and specific. It emphasizes that the most frequent participation level is consultation, involving seeking public feedback for decision-making. Risk perception is a common topic in participatory processes, highlighting the importance of understanding and addressing public concerns about activities risks. Understanding risk and questions raised during participation is crucial to studying risk perception. This knowledge can improve policies, identify risk mitigation solutions, and identify relevant questions to aid in logical answers.

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1 Introduction

The petrochemical industry refers to compounds and polymers derived directly or indirectly from gas or crude oil and used in the chemical industry (Matar and Hatch, 2001). Petrochemical clusters entail a wide range of risks either for the environment or the people living alongside them, both on a short-term and a long-term basis (World Health Organization, 2010). The report “Environment and Health Risks: A Review of the Influence and Effects of Social Inequalities” provided by the World Health Organization (WHO, 2010) points to six environmental health challenges: air quality, housing and residential location, unintentional injuries in children, work-related health risks, waste management and climate change, social and gender-related inequalities, and children’s exposure to risks.

In the past decades, several studies have focused on the perception of technological risk derived from the petrochemical industry (e.g., Pasetto, Mattioli, and Marsili, 2019). For example, Fonzo et al. (2022)conducted a review of the existing research on the distribution of health hazards in industrial pollution, and they demonstrated the social dimension of health hazards from industrial contamination. Dettori, Pittaluga, Busonera, Gugliotta, Azara, Piana, Arghittu and Castiglia presented a work aimed at assessing the risk perception and evaluating the community outrage linked to environmental factors among a self-selected sample of citizens living in an area characterized by the presence of industrial structures of high emotional impact (Dettori et al., 2020), and Pasetto, Mattioli, and Marsili (2019) reviewed health inequalities in areas affected by industrially contaminated sites. Some other studies have concentrated on the impact of the petrochemical industry on human health, focusing on potential adverse health outcomes (Bamber et al., 2019), cancer (Domingo et al., 2020).

Through emerging information technology and social media, people’s perception of technological risks derived from industrial complexes has gained new research interest. The appearance of digital platforms offering new participatory channels enables innovative methodologies such as Public Participation Geographic Information Systems (PPGIS). PPGIS is considered to be a field within Geographic Information Science where citizens can use geospatial technologies and generate data to support decision-making processes (Laatikainen et al., 2017). The term PPGIS was first used in 1996 at the National Center for Geographic Information and Analysis meetings in the United States, and its relevance has been emphasized repeatedly (Saadallah, 2020). Brown and Kyttä have conducted literature reviews centred on a deeper understanding of PPGIS’s multiple dimensions (Brown and Kyttä, 2014). There is an agreement in understanding PPGIS as an alternative tool to public participation processes (Sawicki and Peterman, 2002; Weiner et al., 2002; Sieber, 2006; Dunn, 2007; McLain et al., 2013). However, PPGIS has been driven more by the explorations into the potential and the opportunities of new technologies (applied research) than conceptual and theoretical research (basic research), therefore its body of knowledge is heterogeneous in its concept and methods (Brown and Kyttä, 2014).

The main objective of this paper is to analyze how the participatory process is used to approach risk perception in petrochemical clusters, to determine what risks are more commonly studied, and to pinpoint the main outcomes of using participatory techniques to assess risk perception in petrochemical clusters. To do so, we conduct a comprehensive and up-to-date review of peer-reviewed journals published from 2000 to 2022, examine risk perception related to the petrochemical industry, and focus on participatory processes based on spatial digital platforms. Furthermore, this study’s scope includes a wide range of public participation, from minimal involvement, in which community members are simply informed about projects, to more active participation, in which their input is considered in decision-making processes. It seeks to answer the question, how does the participatory process help to explore the perception of the technological risk through the various levels of participation? By examining these various levels of public participation, we hope to shed light on how community involvement shapes, alters, or enhances perceptions of the petrochemical industry.

This paper fills a gap in risk perception studies and contributes to participatory process research and the social impact of petrochemical clusters. Overall, this paper serves as an important resource for researchers, policymakers, and practitioners interested in risk perception assessment and public participation methodologies. By filling a gap in the literature, this paper helps understand the complex interplay between risk perception and public participation and sheds light on how the local community can engage in the risk management process.

After the Methods section, the paper focuses on the type of questions included in PPGIS questionnaires, the way information is extracted and analyzed, and the spatial approach adopted. An analysis of data collection and data analysis methods is conducted, and the main outcomes are summarized.

2 Methods

A scoping review protocol was developed based on the PRISMA-SCR (Preferred Reporting Items for Systematic Reviews and Meta-Analyses Extension for Scoping Reviews) checklist (see supplementary materials) and explanation (Tricco et al., 2018). This method was chosen because scoping reviews are focused on addressing topics where different study designs may be used, which requires a comprehensive systematization of the existing literature.

2.1 Inclusion criteria

2.2 Search strategy and study selection

Papers meeting the inclusion criteria were identified in 3 steps (Figure 1). Firstly 1), a literature search was conducted on Web of Science and SCOPUS using search terms synthesized in search sentences (Table 1). The four key terms were Public Participation, Geographic Information System, Risk Perception, and Petrochemical; a set of synonyms was chosen for each term (Table 2). Afterwards, 2) a prospective search was made in Google Scholar using a sentence with selected keywords used in the papers’ abstracts (perception of risk, technological site, public participation, GIS). Finally, 3) the inclusion/exclusion criteria were applied.

FIGURE 1

These searches resulted in a total of 1,135 articles on WOS and SCOPUS; they were exported into the reference management software, Zotero, and duplicates were removed, resulting in 892 original articles. After an abstract screening, 62 articles were identified. A full-text screening determined that six articles met the inclusion criteria. In addition to utilizing the Web of Science (WOS) and Scopus databases, Google Scholar was also employed as an external database to augment the inclusion of relevant scholarly articles. Given a large number of Google Scholar results (over 100,000 entries, including grey literature), only the first 100 articles from each search were screened, as per Haddaway et al. (2015). Three articles out of those 100 determined by the search query met the inclusion criteria.

Subsequently, the papers meeting the search criteria were reviewed (Wendelboe-Nelson et al., 2019; Jelks et al., 2021). One additional article meeting the inclusion criteria was found by reviewing the literature of the selected papers. Figure 2 shows the screening process.

FIGURE 2

2.3 Data extraction and data synthesis

Data extraction was conducted by producing a data charting form. Only the papers published after the year 2000 onwards were included. Once all exclusion criteria were applied, the data from the remaining studies were charted under the following fields in Tables 3, 4. The first table includes fields of the extracted data about the article such as the name of authors, country, year of publication, and institution (Table 3). The second includes fields of the extracted data on the case of study, the theoretical and methodological approach, the characteristics of the population that responded to the survey, the type of risk analyzed, and the questions included in the survey (Table 4).

3 Results

3.1 Study characteristics

A total of 893 articles based on the search on WOS and SCOPUS were retrieved, of which 62 were included for full-text screening. Six papers fulfilled all established inclusion criteria. Also, based on the Google Scholar search engine, 100 papers were reviewed, and four papers summarized the general information of each study (Table 5). The scoping review found that most of the included papers were published within the last 5 years, with 50% published after 2018 and 20% published between 2014 and 2018. The other studies were published before 2014. The United Kingdom was the most represented country in terms of country of publication, with seven studies, followed by the Netherlands and the United States (Table 5). Almost all the papers were published in high-quality journals (Q1 and Q2), with Journal of Risk Research accounting for 25% of all publications (Table 5).

Table 6 summarises the main study characteristics of each paper based on the search process. Papers 1, 2, 4, 6, 7 and 10 were studied after 2016, papers 5 and 8 between 2010 and 2016, and papers 3 was studied in 2012 and 9 before 2010. Regarding the area of study, most of them took place in Europe, followed by Asia, the United States and Africa. Furthermore, the spatial scale used in the selected papers is only defined in papers; 1, 7, 8, and 10. Papers 1, 7, and 8 used a regional scale for their research, but only paper 10 used a local scale for the analyses.

Table 7 presents the summaries of the theoretical and methodological approaches and case studies. Regarding the theoretical approaches, most of them investigated risk perception together with other related topics (i.e., environmental risk perception, citizen science and governance policies, and risk management). Environmental risk perception refers to an individual’s cognitive assessment of the significance and immediacy of safeguarding the environment, as well as their comprehension of the interdependencies between human beings and the natural world (Zeng et al., 2020). Citizen science is a collaborative approach to scientific research in which members of the general public participate actively in various phases of scientific projects. Environmental risk management involves the systematic identification, evaluation, and mitigation of potential environmental risks.

In terms of methodological approaches, qualitative (interview and observations) and quantitative analyses (questionnaire, online questionnaire, survey) were commonly used; only paper 6 (Covert et al., 2020) used qualitative analyses exclusively, and only paper 2 (Kharytonov et al., 2017) used quantitative analyses exclusively.

Consulting was the most commonly used level of participation in the selected papers, appearing in four of them.

Regarding social characteristics (Table 8), the participatory process was mainly carried out among the residents in the areas under study in most of the papers, although paper 10 (Fatehian et al., 2018) focused on social groups such as children and tourists.

Regarding age, papers 1, 2, 8, 9 and 10 (Kharytonov et al., 2017; Fatehian et al., 2018, 2018; Hung et al., 2020; Bustamante Picón et al., 2022) did not consider respondent representativeness. However, papers 4, 5 and 6 (López-Navarro et al., 2015; Covert et al., 2020; Lyons et al., 2020) were conducted considering people over the age of 18; paper 7 (Bustamante Picón et al., 2022) was based on the participation of people over 16; and paper 3 (Signorino, 2012) focused on participants between 18 and 60 years old. The number of participants in each study was pretty heterogeneous; paper 10 (Fatehian et al., 2018) did not mention the number of participants in the study.

3.1.1 Type of risks

Table 9 summarizes the studies organized by risk and type of risk. Almost all papers focused on technological risk, while papers 1 and 3 (Signorino, 2012; Hung et al., 2020) studied both types of risks (natural and technological risks).

The concept of natural risk is defined as the attribute of a natural manifestation (hazard), the consequences of which can be harmful (vulnerability) to society. Natural risks differ from technological risks in that the cause (hazard) is not (a priori) linked to human activity, but rather to a natural origin. On the contrary, technological or industrial risks have an anthropogenic origin linked to an installation, an infrastructure, or a way of life of a given civilization.

Papers 1 and 3 (Signorino, 2012; Hung et al., 2020) considered natural and technological risks and established links between both types of hazards. Paper 1, for example, mentions potential sources of technological risks that have resulted in increased air pollution (Hung et al., 2020).

Technological risk is defined as the likelihood of physical, social, and financial harm/detriment/loss due to technology aggregated over its entire lifecycle (Renn and Benighaus, 2013). Although clearly defined, the everyday use of this word has a myriad of connotations (Scheer and Ulbig, 2010; Renn, 2017). Technological hazard refers to the threat potential of a technology or its products (i.e., the potential to harm people, nature, capital, or human-made facilities). In public perception, terms such as hazards and risks are often used interchangeably, which provides a unique challenge for risk communication (Scheer and Ulbig, 2010).

The technological risk was examined in nine papers. Paper 2 (Kharytonov et al., 2017) focused on nitrogen and sulphur dioxides produced by metallurgical enterprises as a type of risk that is related to technological risk and increases air pollution; paper 3 (Signorino, 2012) dealt with noise as a type of risk posed by a petrochemical complex; paper 4 (Lyons et al., 2020) focused on pollution from nuclear sites, refineries, and fracking wells; paper 5 (López-Navarro et al., 2015) focused on oily wastes, solid wastes, underwater noise, ballast water, and accidents such as fires and leakages; paper 6 (Covert et al., 2020) concentrated on oil spills from petroleum complexes, while paper 7 (Bustamante Picón et al., 2022) investigated toxic clouds, fires, and explosions; paper 8 (Vangeli et al., 2014) focused on the spread of chemical products in water; paper 9 (Sun et al., 2009) focused on the electrocatalytic oxidation of sodium pentachloro phenate; and paper 10 (Fatehian et al., 2018) focused on wastewater, garbage, oil, and accumulated solid waste from agricultural factories.

4 Analyzing the participatory process questions

Papers pose two main types of questions: general questions such as age, gender, ethnicity, living area, or employment, and specific questions such as risk perception, type of risk, polluted area, health risk perception, or distance to the polluted area. Table 6 shows the type and terms of questions in each paper.

4.1 General questions

Common contextual questions such as age, gender or education level are defined in the participation process in three papers: employment in two papers, and ethnicity and place of residence in one paper. The questions related to employment were frequently asked in the papers due to their relevance to the case study and analyses being conducted. One paper asks for the name of the respondent, and four papers do not make any general questions (Table 10).

4.2 Specific questions

Specific questions tend to be the bulk of the questions asked to participants. They are laid out in a variety of formats such as open-ended questions, closed-ended questions, Likert scale questions, rating questions, participatory mapping questions, and multiple questions. The most common question refers to risk perception, although the type of risk and level of trust in the government also appear (Table 11).

4.2.1 Risk perception

Risk perception refers to the subjective assessment of the probability of a specified type of accident happening and how concerned people are about its consequences (Sjöberg et al., 2004). It also includes evaluations of the probability and consequences of a negative outcome (Sjöberg et al., 2004). Regarding methods, almost all papers rely on surveys and in-depth interviews to assess risk perception; only paper 2 (Kharytonov et al., 2017) used an open interview as a tool for data collection. Papers 1, 3, and 6 (Signorino, 2012; Covert et al., 2020; Hung et al., 2020) used statistical software, such as SPSS and Excel, to analyze answers and outcomes, while papers 2, 5, and 7 (López-Navarro et al., 2015; Kharytonov et al., 2017; Bustamante Picón et al., 2022) ran analyses using their own specific software.

In paper 1 (Hung et al., 2020), there are a variety of questions, including multiple-choice, Likert, and rating scale questions, as well as open-ended questions. Papers 3, 5, and 6 (Signorino, 2012; López-Navarro et al., 2015; Covert et al., 2020) attempt to address the question through the survey by using a variety of queries, including close-ended questions, multiple-choice questions, multiple questions, Likert and open-ended questions. Only paper 7 (Bustamante Picón et al., 2022) focuses on participatory mapping (Table 12) (Figure 3).

FIGURE 3

4.2.2 Trust in the information provided by the government and companies

Citizens’ trust in the government as a whole is a central element in social psychology (Hassan et al., 2020). Trust in government also influences people’s support for government policies during crises, health policies a case in point (Sankar et al., 2003; Hassan et al., 2020). Trust in government information has been approached through surveys, in-depth interviews, and statistical software (Table 12).

4.2.3 Type of risk

Natural hazards are extreme natural phenomena with consequences that can harm natural and man-made environments. They occur worldwide, are rare in a particular location and time, and contribute to the evolution of the Earth’s landscape (Bathrellos et al., 2021; Skilodimou and Bathrellos, 2021). On the other hand, a technological hazard is an anthropogenic hazard that can harm people, the environment, or facilities (Skilodimou and Bathrellos, 2021). Desertification, water and soil pollution/degradation, land use changes, waste, and hazardous material accidents may also be related to technological hazards. Methodologically, these papers rely on open interviews, in-depth interviews, and surveys. Furthermore, the survey and interviews mostly used open-ended questions, multiple-choice questions, rating questions, Likert scale questions, and close-ended questions. In terms of software, paper 2 (Kharytonov et al., 2017) had its own software known as SAMASAFIA, while others used ArcMap, SPSS, and other commercial programs.

4.2.4 Polluted area

Papers 9 and 10 (Sun et al., 2009; Fatehian et al., 2018) elicit from participants where pollution occurs, in order to identify unknown polluted areas (Figure 4). Only the survey and in-depth interview were used as method tools for the publications that addressed the polluted area question. Furthermore, SPSS and Google Maps marker clusters were used as data collection and analysis software.

FIGURE 4

4.2.5 Health risk perception

Perceptions of health-related risks are required in order to take protective action, such as adopting a healthier lifestyle, attending health screenings, and following medical advice (Renner et al., 2015). It appears logical that the greater the perceived risk is to one’s health, the stronger the motivation for protective action appears to be (Renner et al., 2015). As a result, it is critical to comprehend how people perceive health risks, the accuracy of these perceptions, and how information about one’s health risks is received. Papers 6 and 8 (Vangeli et al., 2014; Covert et al., 2020) focus on health risk perception using surveys and in-depth interviews. Some papers used a variety of tools such as paper 8 (Vangeli et al., 2014) where text questions, multiple-choice questions, rating questions, open-ended questions, and close-ended questions were all used in their public participation processes (Table 12).

4.2.6 Distance to the polluted area

Only papers 4 and 7 (Lyons et al., 2020; Bustamante Picón et al., 2022) focus on the distance to a polluted area. Both of them used the survey as a method tool, and paper 4 (Lyons et al., 2020) also used open-ended questions, rating questions, and close-ended questions.

4.2.7 Purpose and outcomes

Table 13 summarizes the purpose and outcomes addressed by each paper during the participatory process. Papers focus on a variety of topics, ranging from risk information (paper 1) to socioeconomic attitudes (paper 3) and environmental issues (e.g., papers 2, 6). However, most papers aim at assessing risk perception, from a myriad of slants (e.g., papers 4, 7, 8, 10).

5 Discussion and conclusion

It has been recognized that public participation and social science are pertinent tools in decision-making and problem-solving (Brown and Kyttä, 2014; Laatikainen et al., 2017); it is also acknowledged that conflicts involving the localization of hazardous facilities should be resolved through collaboration between the agencies or industries involved and those affected (Gouldson and Bebbington, 2007). This dialogue can be achieved by involving the public in a number of processes such as public meetings, citizen panels, or decision-making practices more transparent and democratic (Gouldson and Bebbington, 2007), and public participation activities. The public participation process on digital platforms provides a new approach to planning processes, allowing for greater and more diverse participation than traditional participatory methods (Saadallah, 2020). Despite the growing popularity of digital platforms for public participation, there is still a lack of research on how to effectively measure and analyze risk perception across these environments. While studies have been conducted on risk perception in general, there is a need for more research that specifically focuses on digital participation methods, such as Public Participation Geographic Information Systems (PPGIS) and Volunteered Geographic Information (VGI).

During the process of selecting and filtering the scientific literature (applying the inclusion/exclusion criteria), the number of available articles was considerably reduced; only ten publications were analysed. Thus, it is evident that there are few resources written in English that study the participatory process, petrochemical clusters and technological risk. For this reason, it should be noted that this study is not a comprehensive study of this topic, but it offers some new exploratory perspectives on the use of the participatory process in the perception of technological risk in petrochemical areas. Furthermore, it is considered that there is a need to extend the application of this type of tools in the perception of technological risk.

This paper demonstrates that the most frequently asked questions in PPGIS studies in petrochemical clusters relate to risk perception, followed by questions about perceived risk; this is relevant because it demonstrates the link between petrochemical clusters and various dimensions of risk. Another insight is the potential influence of age and gender in risk perception, as it would appear that outcomes correlated to both variables.

Future research should concentrate on understanding the relationship between social structure and risk perception, and also on the impacts of perceived risks on mental health, including stress and anxiety-related issues. Another pending study should focus on specific areas, such as the impact of noise and smells on the population, and the role of PPGIS procedures to gather this kind of information.

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