Abstract
Plastic in the linear consumption model is frequently manufactured and disposed of, leading to the creation of excessive plastic waste, which has significant consequences for the environment. Single-use food packaging waste is a large constituent of plastic waste that needs to be addressed urgently. The implementation of reusable packaging systems (RPSs) to close the loop of consumption appears to be promising, but the insights into consumers’ willingness to accept them are limited. This research investigates the aspect of consumers’ adoption of RPSs by identifying the particular user acceptance issues and eventually providing a set of design recommendations to address them. The data collection methods are remote interviews, engaging with 42 participants in three iterations, to evaluate three user experiences of RPSs in order to identify the user acceptance issues. After the user acceptance issues are identified in each iteration, the Theory of Attitude-Behaviour-Context is employed to advance the understanding of the acceptance issues. In order to continuously refine the user experiences, insights from design for sustainable behaviour are applied to address the user acceptance issues. The research results include three refined user experiences, four user acceptance issues—namely hygiene, usability, finance and motivation—and design recommendations to address those user acceptance issues. This research may be of interest to packaging professionals, and could be used to design and refine the RPSs to induce consumers’ adoption.
1. Introduction
The production of plastic has increased dramatically during the last few decades. The linear consumption model combined with ineffective waste management approaches has led to excessive plastic waste ending up in nature, causing significant environmental consequences. For instance, there could be an estimated total of 250,000 tonnes of plastic in the ocean, which imperils the marine ecosystem (e.g., it causes damage the biodiversity in the ocean) [1].
Recently, with the impacts of COVID-19, the plastic waste issues became more prominent, because the usage of single-use products such as plastic gloves increased for hygienic purposes. For instance, Peng et al. [2] argued that around 8.4 ± 1.4 million tonnes of pandemic-associated plastic waste have been generated since the outbreak of COVID-19. Laville [3] also reported that the extra plastic waste from COVID-19 weighs 25,900 tonnes, and that it has leaked into the ocean. Amid the global plastic waste, Geyer et al. [4] identified that the primary packaging (the packaging that is in direct contact with the actual products) from the food sectors is the largest constituent; therefore, addressing primary packaging waste is key to effectively solving this plastic waste issue. However, eliminating primary packaging waste is challenging, as no alternatives can be found to replace the roles that packaging plays in protecting, preserving, containing and marketing the products [5].
The responsibility of eliminating the packaging waste should be placed on the business sectors, which are responsible for the development of packaging solutions [6,7]. In recent years, the business sectors provided some technical solutions (e.g., biodegradable materials or enhanced recycling procedures) [8]. However, Löhr et al. [9] argue that these solutions may not effectively address the plastic issues because of the lack of integration of various societal actors.
What would be an effective approach to address plastic packaging waste? Williams and Helm [10] and the Ellen MacArthur Foundation [11] highlight that reuse should be proposed ahead of technical solutions (e.g., recycling, incineration or resource recovery), inferring that implementing the RPSs would be promising and effective. However, the wide implementation of RPSs encounters barriers, one of which is the lack of consideration of consumers’ adoption [12,13,14,15]. Although some studies related to consumers’ adoption of RPSs can be identified, these studies provide fragmented knowledge. For instance, van der Laan and Aurisicchio [16] focused on fast-moving consumer goods in order to understand consumers’ reuse behaviour, and identified four archetypal behaviours. However, their research provides limited insights on how to encourage consumers to perform these four archetypal behaviours. Kunamaneni et al. [17] investigated the gap between attitude and behaviour regarding the reuse of household care products. Although their research offers four guidelines for designing products that consumers are willing to reuse, these guidelines are generic, and are only limited to household products. Bashir et al. [18] conducted research based on consumers’ aspects in order to refine five refill-based solutions by applying tailored information-based strategies. Their research offers knowledge on how information-based strategies can be applied in order to improve consumers’ adoption. However, the use context—which is also an important factor in consumers’ adoption—is not extensively analysed. Greenwood et al. [13] studied consumers’ engagement with food reusable packaging products and identified 13 types of packaging that consumers are more inclined to reuse. However, an explanation of how these 13 types of packaging can be applied to improve consumers’ adoption is needed.
Based on the above arguments, this research identifies a knowledge gap, i.e., the lack of knowledge of how to improve consumers’ adoption of RPSs to address the plastic issues. In order to fulfill this knowledge gap, this research addresses two research questions:
- I.
- What are the user acceptance issues affecting consumers’ adoption of RPSs?
- II.
- What design recommendations can be made to support packaging professionals in addressing the user acceptance issues?
This research adopts an exploratory approach to iteratively evaluate the user experiences of three RPS cases. The research outcomes advance the knowledge of how to improve consumers’ adoption of RPSs. The remainder of this paper is structured as follows: Section 2 offers a theoretical foundation. Section 3 outlines the research methodology. Section 4 presents the overview of the results, the identification of the user acceptance issues, and the analysis of user acceptance issues. Section 5 discusses the outcomes. Section 6 outlines the research limitations, and Section 7 concludes this research by highlighting the research contribution and the future studies
2. Theoretical Foundation
For the analysis of the adoption of RPSs, we reviewed six highly cited behaviour theories in order to understand the pro-environmental behaviour, namely Persuasion Theory (PT), the Theory of Planned Behaviour (TPB), the Theory of Reasoned Action (TRA), the Theory of Norm Activation (TNA), the Theory of Value-Belief-Norm (TVBN), and the Theory of Attitude-Behaviour-Context (TABC). Among these theories, TABC was chosen for the analysis of the adoption of RPSs. TABC (Figure 1) argues that pro-environmental behaviour is a complex and interactive product of internal/attitudinal factors (e.g., personal beliefs, norms and values) and external/contextual factors (e.g., social norms, monetary incentives, and costs) [19]. The strength of this theory is in explaining the behaviour by focusing on the structural interaction or dynamics between the influence of the attitudinal and contextual factors. In particular, this theory claims that when the role that contextual factors play is weak or non-existent, the attitude–behaviour link is strong. On the other hand, when the contextual factors exert a strong influence, the attitude–behaviour link is weak or non-existent [19,20,21]. In a real situation, desired behaviours are likely to be performed when consumers have a positive attitude towards that behaviour and contextual factors facilitate consumers in the performance of that behaviour [22]. This also suggests that the behaviour could be temporal, as the contextual factors may be changed in different locations and at different times [21,22]. TABC was adopted because the application of TABC can enable this research to focus on the contextual factors, which should be important aspects of user experience. However, the identification of the attitudinal and contextual factors that are relevant to the adoption of RPSs would be required. The following text aims to describe the identification of attitudinal and contextual factors by analysing the other five theories, as well as the use phase of RPSs.
Figure 1.
The Theory of Attitude-Behaviour-Context [19].
2.1. Identification of the Attitudinal Factors
This section describes the identification of the attitudinal factors. The outcomes of reviewing the five theories lead to the identification of the attitudinal factors, which are knowledge, attitude and value. These three factors are important because influencing these three factors should theoretically trigger a behaviour change. Table 1 illustrates the behaviour change models and the attitudinal factors.
Table 1.
The behaviour change models and key attitudinal factors.
2.2. Identification of the Contextual Factors
The exploration of the contextual factors needs to be contextualized in the RPSs. Considering that this research explores consumers’ interactions with the physical artefacts in order to receive the offers of RPSs, the product/service and facilities are therefore relevant and can be defined as contextual factors. To clarify, the product refers to the packaging itself, as the actual content of the product was out of the scope of this research. The service refers to the action offered by the business to extend the lifespan of the packaging (e.g., delivery, collection, washing). Because nowadays products and services are always intertwined, it would be better for individuals to evaluate products and services combined together. Therefore, the product and service could be combined as one contextual factor. The facility refers to the contextual equipment (e.g., refill dispensers or empty packaging collection machines) that delivers the offers. Based on the analysis above, knowledge, attitude, and value can be classified as attitudinal factors, and product/service and facilities are defined as contextual factors. The adapted TABC is illustrated in Figure 2.
Figure 2.
The adapted Theory of Attitude-Behaviour-Context [19].
2.3. Behaviour Change Strategies
This section presents the behaviour change strategies based on the insights from Design for Sustainable Behaviour (DfSB) literature. Steg and Vlek [35] identified two types of strategies, namely informational strategies and structural strategies. Both strategies can be applied in order to influence attitudinal and contextual factors. The application of the informational strategies changes consumers’ attitudinal factors (e.g., attitude, perception, cognition and norms), which creates a desire to perform the behaviour through persuasion. An effective persuasion needs to show the credibility of the information sources in order to increase the trust of the message, tailor the message to highlight the benefits of the behaviour, and pinpoint how to overcome the obstacles that prevent people from changing the behaviour [25,36].
The application of the structural strategies helps consumers to perform the behaviour by altering the contextual factors (e.g., facilities, policies and price). The main principle of applying the structural strategies is to demonstrate the benefits of the behaviour change, such as convenience (e.g., the improvement of the availability of the products or services providers helps consumers to access the products/services providers easily). Alternatively, rewarding desired behaviour is also an effective approach [37,38]. The rewards are classified as financial and non-financial. Financial rewards are always self-evident; however, they need to reach a certain threshold in order to trigger the behaviour change [34,39]. Non-financial rewards refer to intangible benefits, such as convenience, a sense of achievement, or emotional satisfaction [34,39,40]. In relation to the elaboration of the structural strategies, Lilley [41] developed eco-feedback, behaviour steering and persuasive technology to direct, maintain and ensure the behaviour change. Eco-feedback directs behaviour change by providing tangible, auditory and visual information which reminds consumers of their consumption of the resources. Behaviour steering triggers the behaviour change by promoting the benefits or constraints. Persuasive technology ensures the behaviour change by altering consumers’ mindsets.
Tang and Bhamra [42] and Bhamra et al. [43] built upon Lilley’s work, and created seven behaviour change strategies: eco-information (informing the consumption of the resources by making it visible, understandable and accessible for consumers, reflecting their consumption behaviour); eco-choice (providing consumers with sustainable options to encourage them to consider their use behaviour); eco-feedback (informing consumers and helping them to socially and environmentally consider their behaviour through real-time feedback); eco-spur (rewarding desired behaviour and punishing undesired behaviour); eco-steer (restraining the consumers in a planned action); eco-technology (using advanced technology to shape consumers’ behaviour in a planned way); and clever design (producing automatic behaviour change through innovative product design).
In contrast to the strategies mentioned above, Lockton et al. [44] proposed a framework containing six sets of strategies or lenses, which are: the architectural lens (changing the layout of a product or service system to influence consumers’ behaviour); the error proofing lens (treating the behaviour that deviated from the desired behaviour as an error); the persuasive lens (employing digital interface to convey information to persuade consumers); the visual lens (using shape, sounds, textures and so on to influence consumers’ behaviour); the security lens (counter-measures to deter or prevent the undesired behaviour); and the cognitive lens (influencing consumers’ decision-making process in order to develop the targeted behaviour).
Moreover, De Medeiros et al. [45] performed a study to evaluate similarities among these aforementioned strategies. Accordingly, the framework was developed to support the process of applying the behaviour change strategies to influence attitudinal and contextual factors. Because the strategies from Steg and Vlek [35] are explicitly related to attitudinal factors and contextual factors, their strategies can be also incorporated into the framework. Table 2 shows the adapted framework, which offers the guidelines for the application of behaviour change strategies to influence attitudinal and contextual factors.
Table 2.
The adaption of the behaviour change framework [45].
3. Research Methodology
The purpose of the research is to investigate the issues affecting consumers’ adoption of RPSs. To this end, an inductive approach was employed to develop theories based on the collected data. This research was focused on three RPS cases (Case 1, Case 2 and Case 3) that require consumers to return the empty packaging, which should significantly challenge user acceptance. The current packaging consumption is based on a linear pattern (purchase, use, disposal), and packaging solutions requiring consumers to return the empty packaging should challenge consumers significantly. Therefore, focusing on this type of RPS cases should generate insights to address the knowledge gap. Case 1, Case 2 and Case 3 were selected because all of them would require consumers to return the empty packaging. Notably, these three cases are examples of three different reusable packaging archetypal models (‘archetypal model’ refers to a group of businesses sharing similar characteristics). Long et al [46] identified 15 archetypal models based on the characteristics (i.e., ownership of the packaging, service types, service locations, target groups and delivery methods). These 15 archetypal models represent all of the variations of RPSs in the market until 2020. It has to be underlined that businesses within same archetypal models may be also different, as identified by Long et al. [46]. These three archetypal models are part of a framework that includes a total of 15 archetypal models, and the insights of this research may only be generalised to those three archetypal models. Table 3 provides the description of these three cases.
Table 3.
The description of these three cases.
Triangulation, which refers to the use of multiple methods to collect data related to the same phenomenon, was adopted in order to enhance the credibility and validity of the collected data [47]. This method helps to ensure that biases arising from the use of a single source are overcome. The data from each case were collected from the company website and two online media articles. First, company websites were visited and relevant information was collected from these websites, including the steps of the user journey, the ownership of the packaging, and the usage scenario. Then, data about the same topics were collected from media articles online. Finally, data from these different resources were compared in order to confirm and support the findings.
Table 4 illustrates the procedures of the research activities, and the following paragraphs describe the procedures.
Table 4.
The procedures of the research activities.
Because this research would involve human participants, ethics approval prior to the data collection was required (Step 1). The Brunel Ethics Committee initially approved this research in February 2020, and additional amendments were subsequently made in March 2020 due to the outbreak of COVID-19. Finally, the data collection was performed by the first author online between April 2020 to July 2020. Prior to the data collection, the research methods were piloted by inviting three Brunel doctoral researchers to pre-test the visualised user experiences and questionnaires (Step 1). These three participants were asked to identify any issues in relation to the clarity of the visualisations and the clearness of the questions. The participants were asked two questions, which were: I. Do you think that these storyboards are easy to understand? II. Do you think that these questions are clear and easy to understand? All of them confirmed that the visualisations and questions were clear and easy to understand. As a result, these visualisations and questions can be considered valid and reliable.
Because the UK is one of the countries generating the largest amount of packaging waste per person, and because people in the UK aged 25–44 are the segment that generates the most plastic waste [48], the research targeted participants in the UK within that age group (Step 1). The messages about the participant recruitment were posted on social media sites such as Facebook and Twitter. The convenience sampling strategy was adopted in order to recruit participants: individuals who fitted the selection criteria and responded positively to the researcher’s posts on social media were invited (e.g., if a person said that he/she felt interested in participating in this research activities, the first author would approach and provide more details about the research purpose, the expectation from the participants, and the research activities, and invite them to participate).
The research protocol was followed in accordance with requirements of the Brunel Ethics Committee (Step 2). Then, the storyboard was explained to the participants (Step 3). Regarding the data collection methods, a semi-structured interview was adopted (Step 4) because it is widely used to gain in-depth information about a complex issue, and to allow new questions into the dialogue [49,50]. The duration of the research activities in each evaluation was controlled to around 30–45 min. In terms of the sample size, the principle of theoretical saturation was used. Theoretical saturation refers to a continuous data collection process until no new information emerges [51,52,53]. Theoretical saturation is also known to be sufficiently achieved between 10 and 15 participants [54]. To clarify, in the first evaluation, the first author initially interviewed 10 participants. Because each participant had produced sufficient data (e.g., all of the participants argued that the return of the empty packaging was an issue), the first author interviewed another 2 participants in order to achieve theoretical saturation. In the second and third evaluation, the first author still initially interviewed 10 participants. Considering that, the user experience was refined, and the participants identified fewer user acceptance issues. The first author interviewed another 5 participants in order to ensure that theoretical saturation was achieved.
Thematic analysis is a flexible approach to analysis, and it provides a rich and detailed account of the data [54,55,56]. The process of performing the thematic analysis followed the six phases introduced by Braun and Clarke [57]. To simplify, the relevant data were initially coded for the extraction of the meaning of the data, themes based on the set of similar codes were identified, and similar themes grouped under the same categorisation were defined as the user acceptance issues. In this way, it was possible to, for example, compare the frequency of the mentioned themes, identify theme occurrence, and graphically display relationships between themes [50,51,52]. This process was carried out in order to analyse all of the data from the participants, leading to the identification of four user acceptance issues (Step 5).
After the user acceptance issues were identified, the analysis of these issues was performed by applying the adapted TABC in order to allocate these four user acceptance issues, resulting in a better understanding of the reasons why consumers cannot accept these RPSs (Step 6). Subsequently, behaviour change strategies were applied to address these issues (Step 7). As this research was iterative, the second and third evaluation followed the same procedure as the first evaluation (Step 8). Finally, design recommendations were developed based on the insights arising from these three evaluations (Step 9).
4. Results
This section provides an overview of the results of the three rounds of user acceptance evaluation, and analyses the identified user acceptance issues.
4.1. Overview of the Results
Table 5 showcases the data in relation to the user acceptance ratings of the three rounds of evaluations. The user acceptance ratings were incrementally improved in each phase of the evaluation, and all of the ratings reached the satisfactory level in the third evaluation, indicating that the application of the behaviour change strategies has allowed the researchers to address the user acceptance issues. It has to be underlined that although “4” was the threshold for consumers to accept, this may only be used as an indication, rather than confirmation that consumers can accept these three RPSs in practice, as this research didn’t invite participants to evaluate these three RPSs in practice. Consequently, when the user acceptance ratings reached “4”, it is suggested that consumers could theoretically accept these offers.
Table 5.
User acceptance ratings for each case, and in each round of evaluation.
4.2. Identification of User Acceptance Issues
The performance of the thematic analysis led to the identification of four major user acceptance issues, and the codes used in the thematic analysis can be found in Appendix B. Table 6 shows the prevalence of the four major issues among the participants in these three evaluations, and the description of each issue is given below.
Table 6.
The prevalence of the four major issues among the participants in these three evaluations.
Hygiene refers to how consumers perceive the hygiene standard of the RPSs. It could be that either consumers consider the offers to be unhygienic, or the offers themselves present hygiene issues. Although hygiene may not be the most frequently mentioned issue, it may be significantly critical. As food products are directly related to human health and safety, it could be inferred that few people would comprise hygiene standards to accept the RPSs.
Usability refers to issues affecting the degree to which the RPSs are easy to use. Consumers usually prefer the offers that are convenient and easy to use, and it can be difficult to dissuade them from this preference. Therefore, this issue may be inevitable, as consumers have to carry out extra activities in order to adopt RPSs. During these three evaluations, the participants commented either that, overall, the offer may have usability issues, or that a specific touchpoint may have a usability issue.
Motivation refers to the specific reasons for consumers to adopt RPSs. In order to change a consumption pattern, consumers must realise benefits from this behaviour change; otherwise, consumers could wonder why they should change their behaviour, if their current consumption pattern is satisfactory.
Finance refers to issues related to payment options (e.g., purchasing and refunding). Most issues related to finance can be regarded as financial risk, and in addition, individuals may have particular preferences related to these financial payment options. Because these RPSs are novel offers with which consumers may be unfamiliar, they may be financially vigilant, as they may perceive the new RPSs as trying to induce them to pay more.
4.3. Addressing the User Acceptance Issues
This section illustrates the application of behaviour change strategies to address the user acceptance issues. First, the adapted TABC was applied in order to allocate these four user acceptance issues (identified in Section 4.2) according to the definitions of the attitudinal and contextual factors. For instance, regarding hygiene issues, some data indicate that participants may have inaccurate knowledge of how the packaging is washed, resulting in the objection to the reusable packaging solutions. Therefore, this issue can be allocated to the attitudinal factor of knowledge. However, other participants may perceive the facilities (e.g., dispenser) as unhygienic, and thus this issue can be allocated onto contextual factor of the facility. Figure 3 shows the allocation of these issues from three evaluations onto the adapted TABC. To clarify, Case 1, Case 2 and Case 3 are represented by C1, C2 and C3. The number in the parentheses refers to the number of participants arguing this issue. The issues of hygiene, finance, motivation and usability are represented by H, F, M, U. The attitudinal (i.e., attitude, value and motivation) and contextual factors (i.e., facility and product/service) are represented by A, V, K, F and P, accordingly. For instance, C1HK (2) refers to two participants arguing that Case 1 has hygienic issues (knowledge factor).
Figure 3.
Mapping of the identified issues considering the adapted Theory of Attitude-Behaviour-Context.
After the mapping process, the adapted behaviour change framework helped us in linking the behaviour change strategies to the attitudinal and contextual factors (see Figure 4). Then, we identified different behaviour change strategies corresponding to each user acceptance issue, and applied these strategies in order to address these issues. Table 7 and Table 8 describe how different behaviour change strategies were applied in order to address the user acceptance issues after the first and second evaluation, respectively.
Figure 4.
Behaviour change strategies grouped in relation to attitudinal and contextual factors.
Table 7.
The behaviour change strategies used to address the user acceptance issues after the first evaluation.
Table 8.
The behaviour change strategies used to address the user acceptance issues after the second evaluation.
5. Discussion of the Results
The application of the behaviour change strategies to address the user acceptance issues resulted in the development of a set of design recommendations, aiming to support packaging professionals in designing the user experience of RPSs. However, these insights may only be applicable for the cases with similar characteristics to the ones that were analysed in this research. Table 9 shows the key characteristics of these three RPSs cases.
Table 9.
The key characteristics of Cases 1, 2 and 3.
5.1. Refined User Experience
This research provided, for each case under analysis, refined user experiences that might increase the user adoption rate. These refined user experiences might support packaging professionals in the design of RPS that share similar key features with the case under analysis. For instance, if the packaging professionals design a user experience that is similar to Case 1, the refined user experience might be used as a source of inspiration. The refined user experiences can be found in Appendix A.
5.2. Design Recommendations to Address These Issues
Design recommendations were developed based on the insights arising from the evaluation and refinement of these three cases. As this research was carried out iteratively, insights (i.e., positive and negative comments from the participants) were received in the different phases of the evaluations, contributing to the development of design recommendations. For instance, in terms of refining the payment methods of Case 2, positive comments on pay-as-you-go and negative comments on pay for subscription suggest that, in order to implement RPSs, businesses may consider pay-as-you-go as the primary payment method, as consumers may not want to be locked into an unfamiliar service. As a result, these insights were analysed and developed into design recommendations. The following sections describe these design recommendations.
5.2.1. Design Recommendations to Address Hygiene Issues
Packaging Professionals Should Consider Giving Live Demonstrations of the Packaging Washing Process
Firstly, hygiene is critically important, and packaging professionals should eliminate consumers’ hygienic concerns. This research identified that reusable packaging that circulates across different consumers can trigger consumers’ concerns about hygiene, which was especially highlighted during the COVID-19 period. The key issue is how to effectively persuade consumers that the reusable packaging is also hygienic. Paradoxically, persuasion can be easily perceived by consumers as a marketing strategy, rather than informing them. This point was endorsed in the second evaluation of Case 1. The original strategy aimed at convincing consumers that the hygienic issues were considered and eliminated through textual and graphic information; however, the participants perceived the information as a marketing strategy, and directly rejected it. This phase of research provided the insights that showing the live demonstration of the packaging washing process can reduce participants’ hygienic concerns, as it can give consumers a feeling that the businesses are honest and show the actual washing process. In order to make the persuasion more effective, packaging professionals could also consider using the information from a credential source to reduce consumers’ hygienic concerns. Both points can be endorsed in the third evaluation of Case 1: the live demonstration of packaging washing process was integrated into Case 1, with the aim to show that the businesses have nothing to hide, and only provide facts to persuade consumers. Moreover, the auditory information about how the washing process was credentialed was given along with the live demonstration of the packaging washing process, leading to the better elimination of hygienic concerns.
Packaging Professionals Should Design the Service in Order to Not Allow People to Access the Packaging if They Don’t Want to Use the Service (Particularly in the Self-Service)
One of the key hygienic issues identified in this research was that consumers might speculate that other people touched the packaging that they use, which may lead to hygienic concerns. For instance, in the first evaluation of Case 1, participants speculated that the bottles openly placed on the table were likely to be frequently touched by other consumers, thereby causing hygienic concerns. The solution should aim to not allow people to access the packaging if they don’t want to use the service. This research provided one solution based on the third evaluation of Case 1: the bottles were kept away from people and managed by employees. Consumers may need to ask employees to use the service, and employees would refill the packaging for consumers. Therefore, this should give consumers a feeling that the bottles would be properly managed, and other consumers could not touch the bottles. Hence, this can lead to the reduction of hygienic concerns.
Packaging Professionals Need to Consider How to Maintain the Hygienic Standard of the Designated Locations for Consumers to Return the Packaging
Consumers returning the empty packaging should be a key service touchpoint. However, this can easily trigger consumers’ concerns about hygienic issues. For instance, in the first and second evaluations of Case 2, when consumers opened the collection box to return the packaging, they could see the unfinished food and packaging piled in the box, and this image triggered consumers’ concerns about the washing process of the packaging and the hygienic standards. One strategy was generated based on the third evaluation of Case 2: a box for consumers to throw the unfinished food into was integrated into the service touchpoint, allowing consumers to throw the unfinished food in the box, contributing to the maintenance of the hygiene standards.
5.2.2. Design Recommendations to Address Usability Issues
Packaging Professionals Should Consider How to Maximize the Availability of the Service Providers
Because RPSs could already be burdensome for consumers to adopt, packaging professionals should consider minimising consumers’ efforts spent on the adoption of the service. The results of this research show that returning the empty packaging is one key challenge that directly influences the convenience of those RPSs. Accordingly, the key consideration should be placed on how to increase the availability of the service providers (e.g., drop-off locations). This strategy is effective, and is endorsed by multiple scholars [17,58,59,60,61,62,63]. This point can be also reflected in the second evaluation of these three cases, as a significantly decreased number of participants argued about the usability after this issue had been addressed. Moreover, the locations to deploy the collection box can be inside the location of the service providers, in order to link the sales with the return of the packaging [62,63]. This is financially beneficial for the business.
Packaging Professionals Should Design the Service to Allow Consumers to Obtain the Instruction Information in a Convenient and Responsive Manner
Some inconveniences prior to the purchase can be highlighted as well. As the RPSs might be novel services that consumers are unfamiliar with, consumers should learn how the new services work. If consumers need to self-learn how to use the services, businesses need to make the textual information concise enough for consumers to absorb quickly. However, some consumers may not be confident in understanding the information in the self-learning format. Therefore, packaging professionals also need to design the service to be responsive to consumers’ questions. For instance, if consumers are not sure about how to use the service, there should be an easy channel for them to ask questions and receive the answers quickly. In the third evaluation of Case 1, the service was further designed by deploying employees to answer questions. Consequently, consumers can take the leaflets to read, understand how the service works, and also ask employees if they have any questions. Latterly, no participant argued this issue.
Packaging Professionals Should Avoid Collecting Consumers’ Personal Data, or Should Collect Only the Personal Data That Are Strictly Necessary
Consumers may consider it inconvenient when the service is designed to collect their personal data (e.g., occupation, email address, or home address). Therefore, packaging professionals should exclude these activities when designing the service. In the first evaluation of Case 2, consumers argued that it was unnecessary and burdensome to offer their personal data to the business. As a result, it is better not to collect customer data if this does not negatively impact service functionality.
Packaging Professionals Should Design the Service to Enable Consumers to Opt out Easily
In order to retain consumers, some businesses make the sign-up process easy but the cancellation process relatively complicated. In terms of the adoption of RPSs, consumers may view a complicated opt-out process as burdensome; this may also cause them to have negative associations with the offers. For instance, in the first evaluation of Case 2, participants had negative perceptions about email cancellation, because they saw this cancellation method as inconvenient. Consequently, packaging professionals should facilitate the opt-out process. In the second evaluation of Case 2, a cancellation function was included in the mobile app in order to facilitate this process, and there was no participant arguing this aspect afterward.
5.2.3. Design Recommendations to Address Motivation Issues
Packaging Professionals Should Provide Financial Benefits in Order to Attract Consumers to Adopt the Services
Although motivation can be influenced by different factors (e.g., benefits, personal pleasure, or a sense of achievement), this research suggests that financial benefits play a significant role and are directly relevant to consumers. For instance, in the second evaluation of Case 1 and Case 2, some participants were arguing what the benefits would be in them adopting the offers. However, when financial benefits (e.g., discounts, vouchers, free trials or promotions) were offered, the participants were motivated to adopt the offers, demonstrating the importance of having the financial benefits.
Packaging Professionals Should Highlight the Environmental Benefits of Consumers’ Adoption, and Should Make Consumers Realise That Their Efforts Can Make a Difference
It may be possible to improve the RPS adoption by highlighting the environmental benefits (e.g., reducing plastic waste to protect the environment). This factor was included in the second evaluations of Case 1, Case 2 and Case 3. The participants were informed that the adoption of these three services can reduce plastic waste, leading to environmental protection. It would also be important for consumers to feel that their efforts can make a difference. For instance, the third evaluation of Case 2 included a scoreboard in the mobile app that highlighted customers’ efforts to reuse packaging. This type of feature can help customers feel that their efforts would be appreciated. Accordingly, packaging professionals should highlight the environmental benefits and incorporate recognition of customers’ efforts in protecting the environment (e.g., reusing packaging) in the design of these RPSs.
5.2.4. Design Recommendations to Address Finance Issues
Packaging Professionals Should Consider Pay-as-You-Go as the Primary Approach to Charging Consumers
Currently, two main approaches are used to charge customers: subscription and pay-as-you-go. This research shows that consumers may prefer pay-as-you-go. In the first and second evaluations of Case 2, the participants argued that they did not want to commit to a service that they were not familiar with. This feeling of unfamiliarity could make consumers view a subscription plan as a commercial strategy to induce them to pay more. Pay-as-you-go is more flexible, and consumers could easily accept this approach. For instance, in the first evaluation of Case 1 and Case 3, the participants had no issues with the pay-as-you-go approach, suggesting that this payment option could be better than the subscription for RPSs.
Packaging Professionals Should Clearly Communicate That the Deposits Are Refundable through Explicit Textual Information
Consumers might have concerns about losing their deposits even if they are informed that the deposit is refundable. In the first evaluation of Case 1, the participants worried that the business might find some excuse (such as damage to the packaging) to refuse to return the deposit. Therefore, it is important to highlight that the deposit is fully refundable. Packaging professionals can use text and/or images to convey this information. In the second evaluation of Case 1, personified texts and rhetorical questions were used to clearly state that the deposits were fully refundable, and no participant argued this issue subsequently.
Packaging Professionals Should Prefer the Deposit Refund System over the Penalty Charge System in Order to Encourage Consumers to Return the Packaging
There are two ways for businesses to encourage customers to return the packaging. First, businesses can charge customers a deposit for the packaging, and this deposit is refunded when the packaging is returned. Alternatively, businesses can use a penalty system in which customers must supply their financial data (e.g., bank account) and businesses then charge consumers for packaging that is returned late or not at all. This research founds that the penalty system might cause issues that affect the adoption of RPSs. In the first evaluations of Case 2 and Case 3, both imposed a charge for packaging that was not returned or returned late. However, some participants said that they wouldn’t use the service due to the possibility of a penalty, and preferred single-use packaging products as a result. The deposit return system may be an easier and less stressful approach. Although this approach may also have some negative aspects, such as inconvenience (e.g., collecting and returning deposits may involve more work), customers are more open to this approach. In the second evaluation of Case 1, after participants were better informed that the deposits were fully refundable, no participants raised issues about the deposits. However, some participants were concerned about the financial charge if they unpunctually returned the packaging, which should refer to the penalty charge system. Therefore, packaging professionals should consider implementing the deposit-refund system.
6. Limitations of This Research
Three limitations were identified. First, the differences between in-person evaluations and virtual evaluations must be acknowledged. In-person evaluations could provide the opportunity to gather more details of the user experiences, and could thus generate more insightful data. For this reason, future research could focus on in-person evaluations (e.g., by using physical packaging and a simulation of the environments where the user experience is supposed to take place). Moreover, although this research provides refined user experiences that consumers may accept theoretically, it remains uncertain that consumers can accept them and continue to use these RPSs in practice. Therefore, in-person evaluations could also provide insights into this aspect.
Second, this research has focused on improving user acceptance on the basis of consumers’ insights. However, the feasibility of implementing any improvements also needs to be validated from the business perspective. For instance, while financial incentives can induce the adoption of RPSs, business insights are important in order to determine which format of financial incentive (e.g., vouchers, product promotions, or price discounts) is most effective, taking into account profit margin loss considerations. As a result, some of the design recommendations may not be viable for businesses to implement.
Finally, although this research identifies the user acceptance issues and develops a set of design recommendations, these insights may be only generalized to certain cases within these three archetypal models. Although some of the user acceptance issues and design recommendations may also be applicable to cases in other archetypal models, this research cannot claim this insight without empirical evidence.
7. Conclusions
The implementation of RPSs is one of the promising solutions to tackle the packaging waste problem, and to achieve a circular plastic economy. Although these solutions are in an early stage of development, the recognition of their positive impact on the environment can lead to the creation of more novel solutions. However, consumer adoption is a key issue that should be focused on for wider implementation. Currently, the literature on this subject is scarce and does not offer an understanding of the issues or how to address these issues. In this study, we explored consumers’ adoption of RPSs by identifying the user acceptance issues, and we presented design recommendations to address them.
This research made two contributions. (1) It appears to be the first study that provides specific user acceptance issues affecting the adoption of RPSs. This research shows that consumers have concerns with issues relating to hygiene, usability, motivation and finance, highlighting the factors which packaging professionals should consider when designing the user experience of RPSs. It is interesting to note that hygienic issues were not anticipated, and could play an important role in influencing consumers’ adoption. As the reusable packaging may be shared across different consumers, the circulation of the packaging may significantly affect consumers’ acceptance of RPSs. This insight was not extensively highlighted in the current literature. (2) It offers a set of design recommendations based on the refinement of these three user experiences to support packaging professionals to address these four user acceptance issues. Packaging professionals include packaging entrepreneurs (professionals who establish the packaging business to offer reusable packaging solutions), packaging consultants, and professionals who deal with packaging aspects as employees in retail, food and beverage, personal care products, or house cleaning products industries. For instance, packaging entrepreneurs could apply these design recommendations to refine their RPSs; packaging consultants can learn from the user acceptance issues and design recommendations to offer advice to their clients about the user acceptance issues to be considered and how to address them. In conclusion, the research outcomes contribute to supporting packaging professionals in the successful implementation of RPSs.
Furthermore, this research provides an alternative approach to exploring the subject of behaviour change. Whereas behaviour change research often adopts quantitative research methods (e.g., surveys) to examine relationships among different behaviour factors [18,64,65,66,67,68], this research sets one of the examples of how to qualitatively investigate the behaviour change subject. The semi-structured interview was applied to identify the issues affecting user acceptance. The Theory of Attitude-Behaviour-Context was adapted and applied in order to analyse the defined user acceptance issues, and the behaviour change strategies from Design for Sustainable Behaviour were used to address these issues, improving consumers’ adoption.
Opportunities for future research should be highlighted as well. First, because we could not focus on all of the archetypal models due to the time constraint, this research only investigated three cases within three archetypal models individually. Therefore, further study could focus on other archetypal models to investigate other cases, in order to identify a wide range of user acceptance issues. Second, although this research refined three user experiences that consumers can accept theoretically, these insights should be developed in practice, evaluating whether consumers can accept them in the practice. One of the possible solutions is to implement service staging or solution enactment (service staging [69] and solution enactment [70] both refer to a method that evaluates the product/sevice by simulating the product/service’s user experience, in which participants can immerse themselves for evaluation) to prototype these refined user experiences and recruit participants to physically use these services in order to understand their acceptance. Third, even if the design recommendations were theoretically confirmed to be useful based on consumers’ perspectives, it was not possible to know the feasibility of the implementation of those strategies based on business perspectives. Further study could also invite participants from the business sectors to practically evaluate those three refined user experiences and design recommendations in order to understand the potential business barriers associated with their adoption.
Author Contributions
Conceptualisation of the paper, Y.L., F.C. and N.T.; methodology, Y.L., F.C. and D.H.; data collection and analysis, Y.L. and F.C.; original draft preparation, Y.L.; writing—review and editing, Y.L., F.C., D.H. and N.T.; visualisation, Y.L. All authors have read and agreed to the published version of the manuscript.
Funding
This research received no external funding.
Institutional Review Board Statement
Not applicable.
Informed Consent Statement
Informed consent was obtained from all subjects involved in the study.
Data Availability Statement
Not applicable.
Conflicts of Interest
The authors declare no conflict of interest.
Appendix A. The User Experience Evaluated in This Research
In order for them to remain anonymous, the companies’ names and logos were removed from the user experience.
Figure A1.
The first version of Case 1.
Figure A1.
The first version of Case 1.

Figure A2.
The second version of Case 1.
Figure A2.
The second version of Case 1.

Figure A3.
The third version of Case 1.
Figure A3.
The third version of Case 1.

Figure A4.
The first version of Case 2.
Figure A4.
The first version of Case 2.

Figure A5.
The second version of Case 2.
Figure A5.
The second version of Case 2.

Figure A6.
The third version of Case 2.
Figure A6.
The third version of Case 2.

Figure A7.
The first version of Case 3.
Figure A7.
The first version of Case 3.

Figure A8.
The second and third versions of Case 3.
Figure A8.
The second and third versions of Case 3.

Appendix B. The Codes and Themes Identified in the Thematic Analysis
Table A1.
Codes and themes in the first evaluation.
Table A1.
Codes and themes in the first evaluation.
| Codes | Themes (The Issues Are Related to …) | User Acceptance Issues |
|---|---|---|
| 1. Question the hygienic standard |
| Hygiene |
| 2. Hygiene is strictly relevant to health | ||
| 3. Uncleaned packaging threatens health | ||
| 4. Concern other people’s use of the packaging is unhygienic |
| |
| 5. Dust flies into bottles and other people touch the bottles |
| |
| 6. Desire to know the washing process |
| |
| 7. Concern whether washing is done properly | ||
| 8. Concern packaging touched by other people | ||
| 9. Too many service touchpoints |
| Usability |
| 10. Consumers value their efforts | ||
| 11. Using this service consumes people’s energy | ||
| 12. Keeping packaging is difficult |
| |
| 13. Carry bottle is inconvenient | ||
| 14. Carry bottles requires efforts | ||
| 15. Heavy bottles | ||
| 16. Girl’s objection towards returning |
| |
| 17. Returning packaging is hard to perform | ||
| 18. Returning is time-consuming | ||
| 19. Why return the packaging | ||
| 20. The availability of drop-off location matters |
| |
| 21. The distance between consumers and drop-off locations is important | ||
| 22. Travel to locations is inconvenient | ||
| 23. Consumers like to stick to what they know |
| |
| 24. Challenging habit | ||
| 25. Issues in buying new products before finish | ||
| 26. Prefer competitors’ service | ||
| 27. Email cancellation burdensome |
| |
| 28. Hard to verify customer’s identify | ||
| 29. Sign-up process is complicated | ||
| 30. Sharing privacy should not be needed | ||
| 31. Embarrassment in standing to know the instruction |
| |
| 32. Standing also affects other consumers | ||
| 33. System hard to understand | ||
| 34. Sharing financial details seems risky |
| Finance |
| 35. Subscription seems financial risky | ||
| 36. Dislike to pay for subscription | ||
| 37. Unreturned packaging is financially risky | ||
| 38. Financial stress in using the service | ||
| 39. Charging consumers’ deposit is hard |
| |
| 40. Feeling of deposit leads to more costs | ||
| 41. Paying deposit is an issue | ||
| 42. Paying deposits seems financially risky | ||
| 43. Paying deposits seems a lack of transparency | ||
| 44. Wonder reason for deposits | ||
| 45. Relatively expensive deposit | ||
| 46. Unsure whether like the service or not before paying for it |
| |
| 47. Service lacks benefits |
| Motivation |
| 48. Lack of the acknowledge of the importance of the service | ||
| 49. Pay for environmental protection doesn’t make sense |
|
Table A2.
Codes and themes in the second evaluation.
Table A2.
Codes and themes in the second evaluation.
| Codes | Themes (The Issues Are Related to …) | Issues |
|---|---|---|
|
| Hygiene |
| ||
| ||
| ||
| ||
|
| |
|
| |
| ||
|
| |
| ||
|
| Usability |
| ||
| ||
| ||
|
| |
|
| |
|
| Finance |
| ||
| ||
|
| |
|
| Motivation |
|
Table A3.
Codes and themes in the third evaluation.
Table A3.
Codes and themes in the third evaluation.
| Codes | Themes (The Issues Are Related to ……) | Issues |
|---|---|---|
|
| Hygiene |
| ||
|
| Usability |
|
| |
|
| Finance |
|
|
References
- Eriksen, M.; Lebreton, L.C.M.; Carson, H.S.; Thiel, M.; Moore, C.J.; Borerro, J.C.; Galgani, F.; Ryan, P.G.; Reisser, J. Plastic Pollution in the World’s Oceans: More than 5 Trillion Plastic Pieces Weighing over 250,000 Tons Afloat at Sea. PLoS ONE 2014, 9, e111913. [Google Scholar] [CrossRef] [PubMed] [Green Version]
- Peng, Y.; Wu, P.; Schartup, A.T.; Zhang, Y. Plastic Waste Release Caused by COVID-19 and Its Fate in the Global Ocean. Proc. Natl. Acad. Sci. USA 2021, 118, e2111530118. [Google Scholar] [CrossRef] [PubMed]
- Laville, S. About 26,000 Tonnes of Plastic COVID Waste Pollutes World’s Oceans–Study|Pollution. Available online: https://www.theguardian.com/environment/2021/nov/08/about-26000-tonnes-of-plastic-covid-waste-pollutes-worlds-oceans-study (accessed on 30 March 2022).
- Geyer, R.; Jambeck, J.R.; Law, K.L. Production, Use, and Fate of All Plastics Ever Made. Sci. Adv. 2017, 3, e1700782. [Google Scholar] [CrossRef] [PubMed] [Green Version]
- Marsh, K.; Bugusu, B. Food Packaging—Roles, Materials, and Environmental Issues: Scientific Status Summary. J. Food Sci. 2007, 72, R39–R55. [Google Scholar] [CrossRef]
- Van Eygen, E.; Laner, D.; Johann, F. Circular Economy of Plastic Packaging: Current Practice and Perspectives in Austria. Waste Manag. 2018, 72, 55–64. [Google Scholar] [CrossRef]
- Phelan, A.; Meissner, K.; Humphrey, J.; Ross, H. Plastic Pollution and Packaging: Corporate Commitments and Actions from the Food and Beverage Sector. J. Clean. Prod. 2022, 331, 129827. [Google Scholar] [CrossRef]
- Heidbreder, L.M.; Bablok, I.; Drews, S.; Menzel, C. Tackling the Plastic Problem: A Review on Perceptions, Behaviors, and Interventions. Sci. Total Environ. 2019, 668, 1077–1093. [Google Scholar] [CrossRef]
- Löhr, A.; Savelli, H.; Beunen, R.; Kalz, M.; Ragas, A.; Van Belleghem, F. Solutions for Global Marine Litter Pollution. Curr. Opin. Environ. Sustain. 2017, 28, 90–99. [Google Scholar] [CrossRef] [Green Version]
- Williams, M.; Helm, A. Waste-to-Energy Success Factors in Sweden and The United States: Analysing the Transferability of The Swedish Waste-to-Energy Model to The United States. Analyzing the Tranferability of the Swedish Waste-to-Energy Model to the United States; George Washington University: Washington, DC, USA, 2011. [Google Scholar]
- Ellen MacArthur Foundation. Reuse-Rethinking Packaging; Ellen MacArthur Foundation: Isle of Wight, UK, 2019. [Google Scholar]
- Coelho, P.M.; Corona, B.; ten Klooster, R.; Worrell, E. Sustainability of Reusable Packaging–Current Situation and Trends. Resour. Conserv. Recycl. X 2020, 6, 100037. [Google Scholar] [CrossRef]
- Greenwood, S.; Walker, S.; Baird, H.M.; Parsons, R.; Mehl, S.; Webb, T.L.; Slark, A.T.; Ryan, A.J.; Rothman, R.H. Many Happy Returns: Combining Insights from the Environmental and Behavioural Sciences to Understand What Is Required to Make Reusable Packaging Mainstream. Sustain. Prod. Consum. 2021, 27, 1688–1702. [Google Scholar] [CrossRef]
- Ketelsen, M.; Janssen, M.; Hamm, U. Consumers’ Response to Environmentally-Friendly Food Packaging—A Systematic Review. J. Clean. Prod. 2020, 254, 120123. [Google Scholar] [CrossRef]
- Testa, F.; Iovino, R.; Iraldo, F. The Circular Economy and Consumer Behaviour: The Mediating Role of Information Seeking in Buying Circular Packaging. Bus. Strateg. Environ. 2020, 29, 3435–3448. [Google Scholar] [CrossRef]
- van der Laan, A.Z.; Aurisicchio, M. Archetypical Consumer Roles in Closing the Loops of Resource Flows for Fast-Moving Consumer Goods. J. Clean. Prod. 2019, 236, 117475. [Google Scholar] [CrossRef]
- Kunamaneni, S.; Jassi, S.; Hoang, D. Promoting Reuse Behaviour: Challenges and Strategies for Repeat Purchase, Low-Involvement Products. Sustain. Prod. Consum. 2019, 20, 253–272. [Google Scholar] [CrossRef]
- Bashir, H.; Jørgensen, S.; Pedersen, L.J.T.; Skard, S. Experimenting with Sustainable Business Models in Fast Moving Consumer Goods. J. Clean. Prod. 2020, 270, 122302. [Google Scholar] [CrossRef]
- Stern, P.C. Toward a Coherent Theory of Environmentally Significant Behavior. J. Soc. Issues 2000, 56, 407–424. [Google Scholar] [CrossRef]
- Odhiambo Joseph, O. Pro-Environmental Consumer Behavior: A Critical Review of Literature. Int. J. Bus. Manag. 2019, 15, 1. [Google Scholar] [CrossRef] [Green Version]
- Okumah, M.; Martin-Ortega, J.; Novo, P.; Chapman, P.J. Revisiting the Determinants of Pro-Environmental Behaviour to Inform Land Management Policy: A Meta-Analytic Structural Equation Model Application. Land 2020, 9, 135. [Google Scholar] [CrossRef]
- Stern, P.C. Information, Incentives, and Pro-environmental Consumer Behavior. J. Consum. Policy 1999, 22, 461–478. [Google Scholar] [CrossRef]
- Hovland, C.; Janis, I.; Kelley, H. Communication and Persuasion; Yale University Press: London, UK, 1953. [Google Scholar]
- Jackson, T. Motivating Sustainable Consumption: A Review of Evidence on Consumer Behaviour and Behavioural Change: A Report to the Sustainable Development Research Network; University of Surrey, Centre for Environmental Strategy: Guildford, UK, 2005. [Google Scholar]
- Moorman, C.; Diehl, K.; Brinberg, D.; Kidwell, K. Subjective Knowledge, Search Locations, and Consumer Choice. J. Consum. Res. 2004, 31, 673–680. [Google Scholar] [CrossRef] [Green Version]
- Ajzen, I.; Fishein, M. Understanding Attitudes and Predicting Social Behaviour; Prentice-Hall: Englewood Cliffs, NJ, USA, 1980; p. 278. [Google Scholar]
- Wong, C.A.; Afandi, S.H.M.; Ramachandran, S.; Kunasekaran, P.; Chan, J.K.L. Conceptualizing Environmental Literacy and Factors Affecting Pro-Environmental Behaviour. Int. J. Bus. Soc. 2018, 19, 128–139. [Google Scholar]
- Ajzen, I. Behavioral Interventions Based on the Theory of Planned Behavior. In Action Control; Springer: Berlin/Heidelberg, Germany, 1985; pp. 11–39. [Google Scholar] [CrossRef]
- Sniehotta, F.F.; Presseau, J.; Araújo-Soares, V. Time to Retire the Theory of Planned Behaviour. Health Psychol. Rev. 2014, 8, 1–7. [Google Scholar] [CrossRef] [PubMed]
- Reser, J.P.; Bentrupperbäumer, J.M. What and Where Are Environmental Values? Assessing the Impacts of Current Diversity of Use of “environmental” and “World Heritage” Values. J. Environ. Psychol. 2005, 25, 125–146. [Google Scholar] [CrossRef]
- Carrington, M.J.; Neville, B.A.; Whitwell, G.J. Why Ethical Consumers Don’t Walk Their Talk: Towards a Framework for Understanding the Gap Between the Ethical Purchase Intentions and Actual Buying Behaviour of Ethically Minded Consumers. Springer Pap. 2010, 97, 139–158. [Google Scholar] [CrossRef]
- Schwartz, S.H. Awareness of Consequences and the Influence of Moral Norms on Interpersonal Behavior. Sociometry 1968, 31, 355. [Google Scholar] [CrossRef]
- Okumah, M.; Ankomah-Hackman, P. Applying Conditional Process Modelling to Investigate Factors Influencing the Adoption of Water Pollution Mitigation Behaviours. Sustain. Water Resour. Manag. 2020, 6, 1–14. [Google Scholar] [CrossRef] [Green Version]
- Stern, P.C.; Dietz, T.; Abel, T.; Guagnano, G.A.; Kalof, L. A Value-Belief-Norm Theory of Support for Social Movements: The Case of Environmentalism. Hum. Ecol. Rev. 1999, 6, 81–97. [Google Scholar]
- Steg, L.; Vlek, C. Encouraging Pro-Environmental Behaviour: An Integrative Review and Research Agenda. J. Environ. Psychol. 2009, 29, 309–317. [Google Scholar] [CrossRef]
- Fogg, B. Creating Persuasive Technologies. In Proceedings of the 4th International Conference on Persuasive Technology—Persuasive ’09, Claremont, CA, USA, 26–29 April 2009; p. 1. [Google Scholar] [CrossRef]
- Niedderer, K.; Cain, R.; Clune, S.; Lockton, D.; Ludden, G. Creating Sustainable Innovation through Design for Behaviour Change; University of Wolverhampton: Wolverhampton, UK, 2014. [Google Scholar]
- Geller, S. Actively Caring for the Environment An Integration of Behaviorism and Humanism. Environ. Behav. 1995, 27, 184–195. [Google Scholar] [CrossRef]
- Wever, R.; Van Onselen, L.; Silvester, S.; Boks, C. Influence of Packaging Design on Littering and Waste Behaviour. Packag. Technol. Sci. 2010, 23, 239–252. [Google Scholar] [CrossRef]
- Grilli, G.; Curtis, J. Encouraging Pro-Environmental Behaviours: A Review of Methods and Approaches. Renew. Sustain. Energy Rev. 2021, 135, 110039. [Google Scholar] [CrossRef]
- Lilley, D. Design for Sustainable Behaviour: Strategies and Perceptions. Des. Stud. 2009, 30, 704–720. [Google Scholar] [CrossRef] [Green Version]
- Tang, T.; Bhamra, T. Putting Consumers First in Design for Sustainable Behaviour: A Case Study of Reducing Environmental Impacts of Cold Appliance Use. Int. J. Sustain. Eng. 2012, 5, 288–303. [Google Scholar] [CrossRef]
- Bhamra, T.; Lilley, D.; Tang, T. Design for Sustainable Behaviour: Using Products to Change Consumer Behaviour. Des. J. 2011, 14, 427–445. [Google Scholar] [CrossRef]
- Lockton, D.; Harrison, D.; Stanton, N.A. The Design with Intent Method: A Design Tool for Influencing User Behaviour. Appl. Ergon. 2010, 41, 382–392. [Google Scholar] [CrossRef] [PubMed] [Green Version]
- De Medeiros, J.F.; Da Rocha, C.G.; Ribeiro, J.L.D. Design for Sustainable Behavior (DfSB): Analysis of Existing Frameworks of Behavior Change Strategies, Experts’ Assessment and Proposal for a Decision Support Diagram. J. Clean. Prod. 2018, 188, 402–415. [Google Scholar] [CrossRef]
- Long, Y.; Ceschin, F.; Mansour, N.; Harrison, D. Product-Service Systems Applied to Reusable Packaging Systems: A Strategic Design Tool. Des. Manag. J. 2020, 15, 15–32. [Google Scholar] [CrossRef]
- Yin, R.K. Case Study Research: Design and Methods. Eval. Res. Educ. 1994, 24, 221–222. [Google Scholar] [CrossRef]
- Tiseo, I. UK: Plastic Packaging Waste Concerns. 2017. Available online: https://www.statista.com/statistics/813512/plastic-packaging-waste-concerns-united-kingdom-uk/ (accessed on 26 March 2021).
- Whiting, L.S. Semi-Structured Interviews: Guidance for Novice Researchers. Nurs. Stand. 2008, 22, 35–40. [Google Scholar] [CrossRef]
- Kallio, H.; Pietilä, A.M.; Johnson, M.; Kangasniemi, M. Systematic Methodological Review: Developing a Framework for a Qualitative Semi-Structured Interview Guide. J. Adv. Nurs. 2016, 72, 2954–2965. [Google Scholar] [CrossRef]
- Strauss, A.L.; Corbin, J.M. Grounded Theory Research: Procedures, Canons, and Evaluative Criteria. Qual. Sociol. 1990, 13, 3–21. [Google Scholar] [CrossRef]
- Bloor, M.; Wood, F. Theoretical Saturation; Sage Publications: New York, NY, USA, 2011. [Google Scholar] [CrossRef]
- Rowlands, T.; Waddell, N.; Mckenna, B. A Pragmatic Definition of the Concept of Theoretical Saturation. J. Comput. Inf. Syst. 2016, 56, 40–47. [Google Scholar] [CrossRef]
- Guest, G.; MacQueen, K.; Namey, E. Applied Thematic Analysis; Sage Publications: New York, NY, USA, 2011. [Google Scholar]
- Terry, G.; Hayfield, N.; Clarke, V.; Braun, V. Thematic Analysis; Sage Publications: New York, NY, USA, 2017. [Google Scholar] [CrossRef]
- Alhojailan, M.I. Thematic Analysis: A Critical Review of Its Process and Evaluation. West East J. Soc. Sci. 2012, 1, 39–47. [Google Scholar]
- Braun, V.; Clarke, V. Using Thematic Analysis in Psychology. Qual. Res. Psychol. 2006, 3, 77–101. [Google Scholar] [CrossRef] [Green Version]
- Zachrisson, J.; Boks, C. Exploring Behavioural Psychology to Support Design for Sustainable Behaviour Research. J. Des. Res. 2012, 10, 50–66. [Google Scholar] [CrossRef]
- Abdalkrim, G.M.; Id, R.; Al-Hrezat, S. The Role of Packaging in Consumer’s Perception of Product Quality at the Point of Purchase. Eur. J. Bus. Manag. 2013, 5, 69–82. [Google Scholar]
- Beitzen-Heineke, E.F.; Balta-Ozkan, N.; Reefke, H. The Prospects of Zero-Packaging Grocery Stores to Improve the Social and Environmental Impacts of the Food Supply Chain. J. Clean. Prod. 2017, 140, 1528–1541. [Google Scholar] [CrossRef] [Green Version]
- Ma, X.; Park, C.; Moultrie, J. Factors for Eliminating Plastic in Packaging: The European FMCG Experts’ View. J. Clean. Prod. 2020, 256, 120492. [Google Scholar] [CrossRef]
- Lofthouse, V.; Bhamra, T. APPENDIX 3—An Investigation into the Drivers and Barriers Relating to the Adoption of Refillable Packaging (WR0113: Objective 2, Deliverable for DEFRA Waste and Resources Evidence Programme); Loughborough University: Loughborough, UK, 2009. [Google Scholar]
- Lofthouse, V.; Bhamra, T.A. Refillable Packaging Systems: Design Considerations. In Proceedings of the DESIGN 2006, the 9th International Design Conference, Dubrovnik, Croatia, 15–18 May 2006. [Google Scholar]
- Kalafatis, S.P.; Pollard, M.; East, R.; Tsogas, M.H. Green Marketing and Ajzen’s Theory of Planned Behaviour: A Cross-Market Examination. J. Consum. Mark. 1999, 16, 441–460. [Google Scholar] [CrossRef]
- Abrahamse, W.; Steg, L.; Vlek, C.; Rothengatter, T. A Review of Intervention Studies Aimed at Household Energy Conservation. J. Environ. Psychol. 2005, 25, 273–291. [Google Scholar] [CrossRef]
- Khan, F.; Ahmed, W.; Najmi, A. Understanding Consumers’ Behavior Intentions towards Dealing with the Plastic Waste: Perspective of a Developing Country. Resour. Conserv. Recycl. 2019, 142, 49–58. [Google Scholar] [CrossRef]
- Chin, H.C.; Choong, W.W.; Alwi, S.R.W.; Mohammed, A.H. Using Theory of Planned Behaviour to Explore Oil Palm Smallholder Planters’ Intention to Supply Oil Palm Residues. J. Clean. Prod. 2016, 126, 428–439. [Google Scholar] [CrossRef]
- Aboelmaged, M. E-Waste Recycling Behaviour: An Integration of Recycling Habits into the Theory of Planned Behaviour. J. Clean. Prod. 2021, 278, 124182. [Google Scholar] [CrossRef]
- Kurtmollaiev, S.; Fjuk, A.; Pedersen, P.E.; Clatworthy, S.; Kvale, K. Organizational Transformation Through Service Design: The Institutional Logics Perspective. J. Serv. Res. 2018, 21, 59–74. [Google Scholar] [CrossRef] [Green Version]
- Rosenbaum, L.F.; Kaur, J.; Abrahamson, D. Shaping Perception: Designing for Participatory Facilitation of Collaborative Geometry. Digit. Exp. Math. Educ. 2020, 6, 191–212. [Google Scholar] [CrossRef]
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