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Article

Factors Influencing the Purchase Intention for Recycled Products: Integrating Perceived Risk into Value-Belief-Norm Theory

Hochschule für Technik und Wirtschaft des Saarlandes (Htw Saar), University of Applied Sciences, Waldhausweg 14, 66123 Saarbrücken, Germany
Sustainability 2022, 14(7), 3877; https://doi.org/10.3390/su14073877
Submission received: 28 January 2022 / Revised: 2 March 2022 / Accepted: 10 March 2022 / Published: 25 March 2022
(This article belongs to the Special Issue Sustainability and Consumer Behaviour)

Abstract

:
Recycling used materials is one way to deal with the depletion of natural resources available on earth. Companies increasingly integrate recycled materials into their production processes and transition towards circular business models. However, although the attitude towards sustainable products is positive, consumers still prefer to buy products made from new instead of recycled materials. Empirical research on factors influencing the purchase intention of recycled products is still limited. This study aims to examine consumers’ individual factors that are important in the decision process to buy recycled products. The Value-Belief-Norm (VBN) theory is explored in the context of recycled product purchase intention. Perceived risk is added to the research model as a moderator that hinders purchase intention. The different influences are analyzed using partial least squares structural equation modelling with a sample of 177 respondents from Germany. Results indicate that the causal chain of relationships between values, beliefs, and personal norm has a positive influence on recycled product purchase intention. Perceived risk, on the other hand, has a significant negative direct effect on purchase intention but strengthens the relationship between personal norms and purchase intention. Theoretical and managerial implications as well as avenues for further research are discussed.

1. Introduction

The number of natural resources available on earth is limited and humans consume much more than what can be recovered. In 2021, “Earth Overshoot Day” was on 29 July, indicating that all ecological resources that could be restored within one year were used up five months before the end of the year [1]. One way to address the problem of overusing natural resources is integrating recycled materials into the production process of new products. Some of the most common examples of recycling are PET plastic bottles or recycled paper. However, there is a strong shift toward using recycled materials in other areas of consumer goods. For instance, the clothing store chain H&M aims to use 30% recycled materials in their clothes by 2025 [2]. This is an example for the efforts companies make to use resources in a sustainable way. However, extant research shows that consumers have a lower willingness to pay for recycled products than for products made from new materials [3], suggesting an increased perceived risk associated with recycled products [4]. The important question, besides the scale of integrating recycled materials into production processes, is if consumers value such efforts. This paper explores the antecedents of purchase intention of recycled products.
Recycled products can be classified as green products [5]. Previous qualitative and quantitative research has extensively analyzed factors influencing consumers to purchase green products (e.g., [6,7]). In the context of recycled products, Bigliardi et al. [8] proposed an integrative theoretical framework including 20 constructs that influence the purchase intention of recycled products. These authors emphasize the importance of green consumption drivers on the individual level. Research on pro-environmental consumer behavior has extensively focused on studying the effect of subjective norms; however, the influence of personal norms is less considered [9]. Whereas people with high subjective norms base their actions on other peoples’ opinions, personal norms describe a feeling of personal obligation towards a certain behavior [10]. This study focuses on personal norms as a direct lever towards purchase intention. To analyze the effect, the Value-Belief-Norm (VBN) theory [11] is applied. The VBN theory suggests that “green behaviours are more likely to occur when a causal series of variables (i.e., values, beliefs, and personal norms) is present” [12] (p. 2). To the author’s knowledge, the VBN model has not yet been discussed and empirically tested for the purchase intention of recycled products. Following Kiatkawsin and Han [13], who explored the intention to behave sustainably, this study uses intention as outcome variable in the VBN model. Additionally, previous research found a negative effect of perceived risk on green product purchase intention [14]. Apart from the direct effect, the author assumes that perceived risk can potentially alter the relationship between personal norms and purchase intention [15]. As an extension to the VBN model, perceived risk is added as a moderator.
The objective of this paper is to empirically test if the VBN model can be applied to the context of recycled product purchase intention. Furthermore, the different effect sizes and their strengths in the causal relationship are explored. As extension of the model, the moderating role of perceived risk is analyzed. This study adds to the existing literature on individual factors influencing consumers’ green purchase intention. On the one hand, it extends the knowledge about recycled products and on the other hand, it evaluates how values, beliefs, norms, and perceived risk effect purchase intention.
The paper is structured as follows: Section 2 conceptualizes recycled products and provides an overview of studies analyzing recycled product purchase intention. Furthermore, in this section the research model is established, and hypotheses are developed based on the VBN theory and perceived risk theory. Section 3 provides the research methodology and the measures used for the structural equation model. In Section 4, the study results of the measurement model, the structural model, and the moderating effect are presented. Section 5 discusses the findings and includes theoretical contributions and managerial implications as well as limitations and opportunities for further research.

2. Conceptual Framework and Hypotheses

2.1. Recycled Products

Recycling is the practice of reusing materials from used products, instead of unused raw materials, and turning them into new products of the same quality [16]. In contrast, upcycling refers to reusing materials to make products of better quality and downcycling creates products of lesser value [17]. Apart from conserving the limited natural resources available on earth, recycling has several other substantial environmental benefits including reducing pollution (in water and air), greenhouse gases, and waste [18]. Companies integrate the circular economy business model, where instead of following a wasteful “take-make-dispose” mentality, they retain used products from consumers and re-enter them into a loop system of reuse [19]. This shift to circular products comes with new product or service characteristics that alter the customer experience [20]. Despite the environmental benefits, consumers have a lower willingness-to-pay for recycled products than for the same products made from new materials [3]. This shows that it is important to further explore factors that influence consumers to purchase recycled products. So far, only a limited number of studies have been conducted to find triggers, especially on consumers’ characteristics, for recycled product purchase intention (Table 1).

2.2. Value-Belief-Norm Theory (VBN)

Individual factors play a central role in the behavioral process of consumers [8]; therefore, this study applies the VBN theory to explore aspects that influence recycled product purchase intention. The VBN theory was developed and first introduced by Stern et al. [11] in the context of social movement support. In this theory, values (altruistic, biospheric, egoistic) impact beliefs (ecological worldview, awareness of consequences and ascription of responsibility). These beliefs influence personal norms, which finally affect behavior. Initially developed to evaluate environmentalism, VBN has been further used to empirically analyze green product purchase behavior such as for cosmetic products [30], sustainable travel mode choice [31], and “alternative fuel vehicles” [32]. For the category of recycled products, to the authors’ knowledge, the model has not been empirically tested.
Values can be described as a belief which people base their actions on and how they evaluate certain situations [33]. In the context of recycled products, there are two relevant values: biospheric and altruistic values [8]. Both these values fall under the category of self-transcendence values [34]. People with high biospheric values care about the effect of their actions on the nature and the ecosystem, whereas people with high altruistic values put the well-being of others first [35]. In the original VBN theory, these two values could not be clearly distinguished from each other, resulting in the use of the biospheric-altruistic value orientation as one variable [36]. However, following theoretical explanations, De Groot and Steg [33] provided empirical evidence that biospheric and altruistic values should be analyzed separately. Furthermore, Rahman and Reynolds [37] found that biospheric values are a stronger motivator for pro-environmental purchase intention than altruistic values. Biospheric and altruistic values are predictors of and have a positive influence on environmental concern [38]. Environmental concern is a general stance and concern towards protecting the environment [39]. Based on extant research that support the positive relationship between self-transcendence values and environmental concern, e.g., [40,41], the following hypotheses are formulated:
Hypothesis 1a (H1a).
Biospheric values positively influence environmental concern.
Hypothesis 1b (H1b).
Altruistic values positively influence environmental concern.
Considering the belief part of the VBN theory, apart from environmental concern, awareness of consequences and ascription of responsibility fall under this category. Awareness of consequences is described as the understanding of individuals about the consequences that environmental problems entail [42]. Ascription of responsibility, on the other hand, comprises who is blamed for the consequences of certain actions or situations [11]. Personal norms are the self-constructed behavioral expectations that an individual puts on themself in different situations [43]. Both, awareness of consequences and ascription of responsibility, are antecedents of personal norms, as they trigger the activation of this mindset [44]. The Norm Activation Model [43] postulated a causal chain of relationships where higher awareness of consequences leads to a greater ascription of responsibility, which in turn increases personal norms [45]. The dependent variable in this study is purchase intention. According to Sheeran [46] (p. 1), “the most immediate and important predictor of a person’s behavior is his/her intention to perform it”. In the VBN framework, personal norms, when activated, have a direct influence on purchase intention and behavior, e.g., [47,48]. Based on this, the following hypotheses are proposed:
Hypothesis 2 (H2).
Environmental concern positively influences awareness of consequences.
Hypothesis 3 (H3).
Awareness of consequences positively influences ascription of responsibility.
Hypothesis 4 (H4).
Ascription of responsibility positively influences personal norms.
Hypothesis 5 (H5).
Personal norms positively influence purchase intention.

2.3. Perceived Risk Theory

Perceived risk, defined as “the expectation of losses associated with purchase” [49] (p. 187), is an important factor in the consumer buying and choice process [50]. Perceived risk has a long history in consumer research and is typically constructed of six types of risks: social, financial, physical, performance, time-related, and psychological risk [51]. All six types of risk can also be present when purchasing recycled products. Table 2 shows perceived risks that could appear in the context of recycled products which are derived from existing literature.
Extant research shows that consumers perceive green products as more expensive and of lower quality than conventional products [64], resulting in financial and performance risk. Furthermore, Essoussi and Linton [4] found that recycled products with high functional risk result in lower willingness-to-pay. Concerning the relationship of risk and personal norms, De Groot and Steg [65] discovered that perception of risk was a predictor of personal norms in the context of willingness to take actions related to nuclear energy. Additionally, previous research in the context of voluntourism showed that perceived risk acts as a moderator between personal norms and purchase intention that weakens the effect [15]. In the present study, the author assumes that perceived risk has a negative influence and is added to the model as a moderator that alters the effect of personal norms on recycled product purchase intention. Based on this discussion, the following hypotheses are formulated:
Hypothesis 6 (H6).
Perceived risk has a negative influence on purchase intention.
Hypothesis 7 (H7).
Perceived risk negatively moderates the relationship between personal norm and purchase intention.
Figure 1 presents the research model in the context of recycled products.

3. Method

3.1. Measures

To measure consumers’ intention to purchase recycled products, measurement scales and items were developed based on extant literature. Each construct was measured with reflective indicators. First, altruistic and biospheric values were assessed following De Groot and Steg [33] using six items adapted from Schwartz [66] value survey. Environmental concern was examined using three items from the short version of the New Environmental Paradigm scale [67] adapted from Stern et al. [11]. To examine awareness of consequences, a three-item scale adapted from Ibtissem [68] and Jansson et al. [32] was used. Ascription of responsibility and personal norms were measured with three and four items, respectively, adapted from Ibtissem [68]. Perceived risk was assessed using five items adapted from Wang et al. [69]. Lastly, purchase intention for recycled products was measured with three items adapted from Lee and Lee [70]. All items were measured on a five-point Likert scale ranging from 1, strongly disagree, to 5, strongly agree. Only altruistic and biospheric values were measured on a five-point Likert scale ranging from 1, very unimportant to 5, very important. For a complete list of the constructs, corresponding items and sources see Table 3.

3.2. Data Collection and Sample

To evaluate the VBN theory in the context of recycled product purchase intention, an online survey was conducted. The completion of the questionnaire took approximately ten minutes. Respondents were ensured that their answers are handled with confidentiality and anonymity. The survey included a short description of recycled products and four examples for better understanding: clothes from fabric remnants, jeans from denim scraps, notebooks and printer paper from recycled paper, and furniture from recycled waste wood. These examples were given to ensure that the focus of this study is on consumer goods and not on packaging. Data collection was conducted in September 2021. The panel provider Clickworker was used to retain a sample size of 200 respondents from Germany. To ensure survey quality, incomplete datasets and respondents who took less than five minutes to complete the questionnaire were deleted [71]. A final sample of 177 respondents remained. Of these respondents, 48% were male and 52% were female, with the majority being in the middle age group 30–49 (62.1%), followed by the 50+ (20.3%) and the 19–29 year-old age group (17.5%). In terms of household income, we saw a fairly even distribution in the sample (13.6% up to 1500€, 11.3% between 1500€ and 2000€, 26% between 2000€ and 3000€, 18.6% between 3000€ and 4000€, 10.2% between 4000€ and 5000€, and 10.7% more than 5000€, with 9.6% not being specified). Most participants’ highest degree of education was baccalaureate (28.8%), followed by secondary school (23.7), bachelor’s degree (19.2%), diploma (13.0%), master degree (11.3%), and lower secondary school (4.0%).

3.3. Statistical Analysis

For the analysis and the calculations of the research model partial least squares structural equation modeling (PLS-SEM) in SmartPLS 3 [72] was used. This variance-based approach, instead of a covariance-based SEM, was chosen for several reasons: First, it allows small sample sizes while still achieving high levels of statistical power [73]. Regarding sample size, the ‘10 times rule’ provides that “the sample size should be greater than 10 times the maximum number of inner or outer model links pointing at any latent variable in the model” [74] (p. 232). In this model the largest number of paths is five, validating that the sample size is well above the minimum number of participants. Second, PLS-SEM makes no particular assumptions about the data and allows nonnormal data [75]. According to the Kolmogorov-Smirnov test, this is the case for this sample. Lastly, PLS-SEM is the preferred method for exploration and prediction [76]. Even though the model of this study is based on an established theory (VBN model), this research can be considered exploratory, as it analyzes the influence of perceived risk in the framework.
To test the validity and reliability of constructs with the corresponding items in the measurement model, the PLS-algorithm path weighting scheme with 300 iterations and a stop criterion of 10−7 [73] was used. For significance testing of the indicator loadings, as well as for path coefficients in the structural model, complete bootstrapping with 5000 subsamples was performed [73].

4. Data Analysis Results

4.1. Measurement Model

All constructs included in the model show one-factor solutions with factor loadings well above 0.5, Cronbach’s alphas above 0.7, and explained variances above 50%. Convergent validity was assessed using composite reliability (CR) and average variance extracted (AVE). All CR scores were above the threshold of 0.7 [77] and all AVE values were greater than 0.5 [78]. Discriminant validity was determined using the heterotrait-monotrait ratio of correlations (HTMT, Table 4). All values are below the threshold of 0.85 [79]. All constructs were successfully validated, and the results are presented in Table 3. To test for common method variance (CMV), a full collinearity test was conducted. The variance inflation factors (VIFs) for the latent variables were all well below 3.3, which suggests that common method bias is not an issue in this model [80].

4.2. Structural Model

To empirically test the model, structural equation modelling with SmartPLS 3 was used. The model explains 54.6% of variance in consumers’ purchase intention of recycled products (R2 = 0.546). Both biospheric values (H1a, β = 0.197, p < 0.05) and altruistic values (H1b, β = 0.269, p < 0.05) have a significantly positive effect on environmental concern. Environmental concern has a very strong, positive influence on awareness of consequences (H2, β = 0.570, p < 0.01). The effects of awareness of consequences on ascription of responsibility (H3, β = 0.493, p < 0.01) and ascription of responsibility on personal norms (H4, β = 0.346, p < 0.01) are also significantly positive. The last path in the model also shows a significantly positive influence of personal norms on the dependent variable purchase intention (H5, β = 0.455, p < 0.01). Additionally, perceived risk has a very strong, highly significant, negative influence on purchase intention (H6, β = −0.427, p < 0.01). The results are visualized in Table 5.
Regarding the moderation effect, perceived risk is added as a moderator for the relationship of personal norms on purchase intention. A moderator is a third variable that alters the relationship of two other variables by either strengthening, weakening, or even changing the direction of the effect [73]. Results show that perceived risk has a large effect (f2 ≥ 0.025, [73,81]) on the relationship between personal norms and purchase intention, which is significant on a 10% level (t-value = 1.899). This means that higher perceived risk generally strengthens the relationship between personal norms and purchase intention, contradicting H7.

4.3. Control Variables

Statistical control variables were included into the analysis to preclude other possible explanations for the findings [82]. It was controlled for gender, age, and social desirability. In the context of green product purchase intention, socially desirable responding could be a potential issue [83]. To control for social desirability bias, a short, true or false, ten-item-version of the Crowne & Marlowe [84] Social Desirability Scale adapted from Strahan and Gerbasi [85] was included. For the first five answers, true, and for the last five answers false indicated socially desirable answering. The sum of socially desirable answers was calculated, ranging from 0 to 10, with a higher score indicating social desirability. All three controls did not have a significant effect on the results (see Table 5).

5. Discussion

This study was designed to get a better understanding of consumers’ purchase intention of recycled products and empirically test the influence of values, beliefs, norms, and perceived risk in this context. Results show that the VBN theory, and thus values, beliefs, and norms have strong predictive power for the purchase intention of recycled products. This is consistent with the findings of Kiatkawsin and Han [13] in the context of pro-environmental behavior and Quoquab et al. [30] for green purchase behavior of cosmetics. In general, this model of the VBN theory, including perceived risk, explains a high amount of variance of the purchase intention of recycled products (R2 = 0.546), which is above the usual 19–35% that this theory explains [86].
Perceived risk, as expected, has a very strong, significantly negative effect on recycled product purchase intention. This is consistent with extant research for other green products, e.g., refurbished products [14]. One counterintuitive finding is that perceived risk moderates the relationship between personal norms and purchase intention in a positive way. Previous research in the context of voluntourism shows contrary results, where if the perceived risk increases, the effect between personal norms and intention weakens [15]. In the present findings, even though the perceived risk of recycled products has a direct negative influence on purchase intention, it acts like an activator for personal norms. If the perceived risk is high, personal norms has a stronger effect on purchase intention. A possible explanation for this is that the moral obligation to contribute to the protection of the environment outweighs the self-interest of consumers.

5.1. Theoretical Contributions

Considering theoretical implications, this study validates the VBN model for a recycling context. Even though the initial VBN model was developed to analyze behavior [11], the present study shows that the theory can also be used with purchase intention as dependent variable. Furthermore, the VBN theory is extended by integrating perceived risk into the model. The results show a significant influence of perceived risk on purchase intention, that should not be neglected in the consumer buying behavior research. Additionally, this study uncovered a significant relationship between perceived risk and the effect of personal norms on purchase intention. In this regard, the findings of the present paper underline the need to include and simultaneously analyze product and individual-related factors in research models [8]. This combination would provide a deeper insight into consumers’ green product purchase intention.

5.2. Managerial Implications

From a managerial point of view, it is crucial to minimize the perceived risk of recycled products, as it is a key factor for increasing sales and thus, for corporate success. Companies should apply different methods to increase trust in their green products, e.g., provide certificates or testimonials, work with influencers who are convinced of a products’ worth, and ensure guarantees [87]. Additionally, this study can help companies to improve their marketing strategy with content that encourages green consumer behavior. Advertisements should appeal to the awareness of consequences and ascription of responsibility of consumers, as these are important triggers of personal norm [44]. If consumers are aware of the consequences that their behavior has and take responsibility for it, they are going to be more likely to buy green products. Lee et al. [88] found negatively framed information to be most successful for consumers’ understanding, remembering and in turn performing sustainable behavior. Negatively framed messages convey the negative consequence of not performing a certain behavior, whereas positively framed messages focus on the positive outcome if a certain behavior is performed [89]. For recycled product purchases, advertisements should appeal to the negative consequences that wasting natural resources have on the environment. These kinds of advertisements enhance personal norms, which is also validated in the context of recycling-aiding products [90]. This is also relevant for institutions or government actions that are promoting green consumption to reach their climate protection goals. Additionally, regulations to oblige companies to use a certain percentage of recycled materials in their products should be implemented.

5.3. Limitations and Future Research

There are some limitations to this study that can be used as avenues for further research. First, only a linear causal chain of relationships between values, beliefs, and norms has been tested in this model. Further research might want to test the direct effects of all variables on purchase intention in order to compare effect strengths and find additional relationships in terms of moderators and mediators. This research also focused on purchase intention as the dependent variable; future studies should test the presented framework for actual purchase behavior. Since this questionnaire was solely distributed in Germany, future replications should be conducted in different countries to analyze potential cultural differences, especially on the relationship between values and environmental concern. Additionally, it would be interesting to explore the purchase intention of specific recycled product types, as this research focuses on recycled products in general. Testing up- and downcycling products could potentially also lead to different findings. Furthermore, the different types of risks associated with recycled products need to be analyzed as well as effective methods to reduce these risks. Lastly, there are many more individual, but also product and context related variables [8] and theories influencing purchase intention. These can be integrated into the VBN theory to get a more complete picture of consumers’ recycled product purchase intention.

Funding

This research was funded by the Saarland State Research Funding Program, grant number 20/14 WiWi.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

All subjects gave their informed consent for inclusion before they participated in the study.

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Acknowledgments

The author would like to thank her supervisor Tatjana König for her support and helpful comments on the paper.

Conflicts of Interest

The author declares no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.

References

  1. Lin, D.; Wambersie, L.; Wackernagel, M. Estimating the Date of Earth Overshoot Day 2021. 2021. Available online: https://www.overshootday.org/content/uploads/2021/06/Earth-Overshoot-Day-2021-Nowcast-Report.pdf (accessed on 24 January 2022).
  2. Troberg, A.; Söderlund, C. Sustainability Performance Report 2020. 2021. Available online: https://hmgroup.com/wp-content/uploads/2021/03/HM-Group-Sustainability-Performance-Report-2020.pdf (accessed on 24 January 2022).
  3. Pretner, G.; Darnall, N.; Testa, F.; Iraldo, F. Are consumers willing to pay for circular products? The role of recycled and second-hand attributes, messaging, and third-party certification. Resour. Conserv. Recycl. 2021, 175, 105888. [Google Scholar] [CrossRef]
  4. Essoussi, L.H.; Linton, J.D. New or recycled products: How much are consumers willing to pay? J. Consum. Mark. 2010, 27, 458–468. [Google Scholar] [CrossRef]
  5. Sdrolia, E.; Zarotiadis, G. A comprehensive review for green product term: From definition to evaluation. J. Econ. Surv. 2019, 33, 150–178. [Google Scholar] [CrossRef] [Green Version]
  6. Joshi, Y.; Rahman, Z. Factors affecting green purchase behaviour and future research directions. Int. J. Manag. Rev. 2015, 3, 128–143. [Google Scholar] [CrossRef] [Green Version]
  7. Wijekoon, R.; Sabri, M.F. Determinants that influence green product purchase intention and behavior: A literature review and guiding framework. Sustainability 2021, 13, 6219. [Google Scholar] [CrossRef]
  8. Bigliardi, B.; Campisi, D.; Ferraro, G.; Filippelli, S.; Galati, F.; Petroni, A. The intention to purchase recycled products: Towards an integrative theoretical framework. Sustainability 2020, 12, 9739. [Google Scholar] [CrossRef]
  9. Onel, N. Pro-environmental purchasing behavior of consumers. Soc. Mark. Q. 2016, 23, 103–121. [Google Scholar] [CrossRef]
  10. Krettenauer, T.; Lefebvre, J.P. Beyond subjective and personal: Endorsing pro-environmental norms as moral norms. J. Environ. Psychol. 2021, 76, 101644. [Google Scholar] [CrossRef]
  11. 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]
  12. Ghazali, E.M.; Nguyen, B.; Mutum, D.S.; Yap, S.F. Pro-environmental behaviours and value-belief-norm theory: Assessing unobserved heterogeneity of two ethnic groups. Sustainability 2019, 11, 3237. [Google Scholar] [CrossRef] [Green Version]
  13. Kiatkawsin, K.; Han, H. “Young travelers” intention to behave pro-environmentally: Merging the value-belief-norm theory and the expectancy theory. Tour. Manag. 2017, 59, 76–88. [Google Scholar] [CrossRef]
  14. Singhal, D.; Jena, S.K.; Tripathy, S. Factors influencing the purchase intention of consumers towards remanufactured products: A systematic review and meta-analysis. Int. J. Prod. Res. 2019, 57, 7289–7299. [Google Scholar] [CrossRef]
  15. Pangaribuan, C.H.; Manurung, A.H.; Saroso, H.; Rusmanto, T. The personal norm-experience intention nexus: Exploring moderator effect of risk perception in voluntourism. ICIC Express Lett. 2022, 13, 123–131. [Google Scholar] [CrossRef]
  16. Gaur, J.; Subramoniam, R.; Govindan, K.; Huisingh, D. Closed-loop supply chain management: From conceptual to an action oriented framework on core acquisition. J. Clean. Prod. 2017, 167, 1415–1424. [Google Scholar] [CrossRef]
  17. Wilson, M. When creative consumers go green: Understanding consumer upcycling. J. Prod. Brand Manag. 2016, 25, 394–399. [Google Scholar] [CrossRef]
  18. Beasley, J.; Georgeson, R.; Arditi, S.; Barczak, P. Advancing Resource Efficiency in Europe: Indicators and Waste Policy Scenarios to Deliver a Resource Efficient and Sustainable Europe. 2014. Available online: https://makeresourcescount.eu/wp-content/uploads/2014/11/FINAL_Advancing-Resource-Efficiency-in-Europe_PUBL.pdf (accessed on 24 January 2022).
  19. MacArthur, E. Towards the circular economy. J. Ind. Ecol. 2013, 2, 23–44. [Google Scholar]
  20. Ta, A.H.; Aarikka-Stenroos, L.; Litovuo, L. Customer experience in circular economy experiential dimensions among consumers of reused and recycled clothes. Sustainability 2022, 14, 509. [Google Scholar] [CrossRef]
  21. Calvo-Porral, C.; Lévy-Mangin, J.P. The circular economy business model: Examining consumers’ acceptance of recycled goods. Adm. Sci. 2020, 10, 28. [Google Scholar] [CrossRef]
  22. Chaturvedi, P.; Kulshreshtha, K.; Tripathi, V. Investigating the determinants of behavioral intentions of generation Z for recycled clothing: An evidence from a developing economy. Young Consum. 2020, 21, 403–417. [Google Scholar] [CrossRef]
  23. Chi, T.; Ganak, J.; Summers, L.; Adesanya, O.; McCoy, L.; Liu, H.; Tai, Y. Understanding perceived value and purchase intention toward eco-friendly athleisure apparel: Insights from U.S. Millennials. Sustainability 2021, 13, 7946. [Google Scholar] [CrossRef]
  24. Luu, T.T.A.; Baker, J.R. Exploring consumers’ purchase intention of rPET bottle-based apparel in an emerging economy. J. Open Innov. Technol. Mark. Complex. 2021, 7, 22. [Google Scholar] [CrossRef]
  25. Magnier, L.; Mugge, R.; Schoormans, J. Turning ocean garbage into products–Consumers’ evaluations of products made of recycled ocean plastic. J. Clean. Prod. 2019, 215, 84–98. [Google Scholar] [CrossRef]
  26. Nguyen, X.H.; Tran, H.L.; Nguyen, Q.H.; Luu, T.P.A.; Dinh, H.L.; Vu, H.T. Factors influencing the consumer’s intention to buy fashion products made by recycled plastic waste. Manag. Sci. Lett. 2020, 10, 3613–3622. [Google Scholar] [CrossRef]
  27. Park, H.J.; Lin, L.M. Exploring attitude–behavior gap in sustainable consumption: Comparison of recycled and upcycled fashion products. J. Bus. Res. 2020, 117, 623–628. [Google Scholar] [CrossRef]
  28. Queiroz, F.C.B.P.; Lima, N.C.; da Silva, C.L.; Queiroz, J.V.; de Souza, G.H.S. Purchase intentions for brazilian recycled PET products—Circular economy opportunities. Recycling 2021, 6, 75. [Google Scholar] [CrossRef]
  29. Sun, H.; Teh, P.L.; Linton, J.D. Impact of environmental knowledge and product quality on student attitude toward products with recycled/remanufactured content: Implications for environmental education and green manufacturing. Bus. Strategy Environ. 2018, 27, 935–945. [Google Scholar] [CrossRef]
  30. Quoquab, F.; Jaini, A.; Mohammad, J. Does it matter who exhibits more green purchase behavior of cosmetic products in Asian culture? A multi-group analysis approach. Int. J. Environ. Res. Public Health 2020, 17, 5258. [Google Scholar] [CrossRef]
  31. Lind, H.B.; Nordfjærn, T.; Jørgensen, S.H.; Rundmo, T. The value-belief-norm theory, personal norms and sustainable travel mode choice in urban areas. J. Environ. Psychol. 2015, 44, 119–125. [Google Scholar] [CrossRef]
  32. Jansson, J.; Marell, A.; Nordlund, A. Exploring consumer adoption of a high involvement eco-innovation using value-belief-norm theory. J. Consum. Behav. 2011, 10, 51–60. [Google Scholar] [CrossRef]
  33. De Groot, J.I.M.; Steg, L. Value orientations to explain beliefs related to environmental significant behavior: How to measure egoistic, altruistic, and biospheric value orientations. Environ. Behav. 2008, 40, 330–354. [Google Scholar] [CrossRef]
  34. Bouman, T.; Steg, L.; Kiers, H.A. Measuring values in environmental research: A test of an environmental portrait value questionnaire. Front. Psychol. 2018, 9, 564. [Google Scholar] [CrossRef]
  35. Wang, X.; Van der Werff, E.; Bouman, T.; Harder, M.K.; Steg, L. I am vs. we are: How biospheric values and environmental identity of individuals and groups can influence pro-environmental behaviour. Front. Psychol. 2021, 12, 618956. [Google Scholar] [CrossRef]
  36. Stern, P.C.; Kalof, L.; Dietz, T.; Guagnano, G.A. Values, beliefs, and proenvironmental action: Attitude formation toward emergent attitude objects. J. Appl. Soc. Psychol. 1995, 25, 1611–1636. [Google Scholar] [CrossRef]
  37. Rahman, I.; Reynolds, D. Predicting green hotel behavioral intentions using a theory of environmental commitment and sacrifice for the environment. Int. J. Hosp. Manag. 2016, 52, 107–116. [Google Scholar] [CrossRef]
  38. Schultz, P.W.; Gouveia, V.V.; Cameron, L.D.; Tankha, G.; Schmuck, P.; Franěk, M. Values and their relationship to environmental concern and conservation behavior. J. Cross-Cult. Psychol. 2005, 36, 457–475. [Google Scholar] [CrossRef]
  39. Minton, A.P.; Rose, R.L. The effects of environmental concern on environmentally friendly consumer behavior: An exploratory study. J. Bus. Res. 1997, 40, 37–48. [Google Scholar] [CrossRef]
  40. Chua, K.B.; Quoquab, F.; Mohammad, J.; Basiruddin, R. The mediating role of new ecological paradigm between value orientations and pro-environmental personal norm in the agricultural context. Asia Pac. J. Mark. Logist. 2016, 28, 323–349. [Google Scholar] [CrossRef]
  41. Han, H.; Hwang, J.; Lee, M.J. The value–belief–emotion–norm model: Investigating customers’ eco-friendly behavior. J. Travel Tour. Mark. 2016, 34, 590–607. [Google Scholar] [CrossRef]
  42. Hansla, A.; Gamble, A.; Juliusson, A.; Gärling, T. The relationships between awareness of consequences, environmental concern, and value orientations. J. Environ. Psychol. 2008, 28, 1–9. [Google Scholar] [CrossRef]
  43. Schwartz, S.H. Normative influences on altruism. Adv. Exp. Soc. Psychol. 1977, 10, 221–279. [Google Scholar] [CrossRef]
  44. Van Riper, C.J.; Kyle, G.T. Understanding the internal processes of behavioral engagement in a national park: A latent variable path analysis of the value-belief-norm theory. J. Environ. Psychol. 2014, 38, 288–297. [Google Scholar] [CrossRef]
  45. De Groot, J.I.; Steg, L. Morality and prosocial behavior: The role of awareness, responsibility, and norms in the norm activation model. J. Soc. Psychol. 2009, 149, 425–449. [Google Scholar] [CrossRef]
  46. Sheeran, P. Intention—behavior relations: A conceptual and empirical review. Eur. Rev. Soc. Psychol. 2002, 21, 1–36. [Google Scholar] [CrossRef]
  47. Kim, S.H.; Seock, Y.K. The roles of values and social norm on personal norms and pro-environmentally friendly apparel product purchasing behavior: The mediating role of personal norms. J. Retail. Consum. Serv. 2019, 51, 83–90. [Google Scholar] [CrossRef]
  48. Liu, X.; Zou, Y.; Wu, J. Factors influencing public-sphere pro-environmental behavior among Mongolian college students: A test of value–belief–norm theory. Sustainability 2018, 10, 1384. [Google Scholar] [CrossRef] [Green Version]
  49. Peter, J.P.; Ryan, M.J. An investigation of perceived risk at the brand level. J. Mark. Res. 1976, 13, 184–188. [Google Scholar] [CrossRef]
  50. Mitchell, V.W. Understanding consumers’ behaviour: Can perceived risk theory help? Manag. Decis. 1992, 30, 26–31. [Google Scholar] [CrossRef]
  51. Stone, R.N.; Gronhaug, K. Perceived risk: Further considerations for the marketing discipline. Eur. J. Mark. 1993, 27, 39–50. [Google Scholar] [CrossRef]
  52. Kim, I.; Jung, H.J.; Lee, Y. Consumers’ value and risk perceptions of circular fashion: Comparison between secondhand, upcycled, and recycled clothing. Sustainability 2021, 13, 1208. [Google Scholar] [CrossRef]
  53. Barbarossa, C.; Pastore, A. Why environmentally conscious consumers do not purchase green products: A cognitive mapping approach. Qual. Mark. Res. 2015, 18, 188–209. [Google Scholar] [CrossRef]
  54. Essoussi, L.H.; Linton, J.D. Offering branded remanufactured/recycled products: At what price? J. Remanuf. 2014, 4, 24. [Google Scholar] [CrossRef] [Green Version]
  55. Wang, Y.; Wiegerinck, V.; Krikke, H.; Zhang, H. Understanding the purchase intention towards remanufactured product in closed-loop supply chains. Int. J. Phys. Distrib. Logist. Manag. 2013, 43, 866–888. [Google Scholar] [CrossRef]
  56. Bayoumi, A.E. Counterfeit Pesticides. J. Chem. Health Saf. 2021, 28, 232–237. [Google Scholar] [CrossRef]
  57. Kishino, H.; Hanyu, K.; Yamashita, M.; Hayashi, C. Recycling and consumption in Germany and Japan: A case of toilet paper. Resour. Conserv. Recycl. 1999, 26, 189–215. [Google Scholar] [CrossRef]
  58. Connell, K.Y.H. Internal and external barriers to eco-conscious apparel acquisition. Int. J. Consum. Stud. 2010, 34, 279–286. [Google Scholar] [CrossRef]
  59. Hazen, B.T.; Overstreet, R.E.; Jones-Farmer, L.A.; Field, H.S. The role of ambiguity tolerance in consumer perception of remanufactured products. Int. J. Prod. Econ. 2012, 135, 781–790. [Google Scholar] [CrossRef]
  60. Aji, H.M.; Sutikno, B. The extended consequence of greenwashing: Perceived consumer skepticism. Int. J. Bus. Inf. 2015, 10, 433–468. [Google Scholar] [CrossRef]
  61. Gleim, M.R.; Smith, J.S.; Andrews, D.; Cronin, J.J. Against the green: A multi-method examination of the barriers to green consumption. J. Retail. 2013, 89, 44–61. [Google Scholar] [CrossRef]
  62. Adigüzel, F.; Donato, C. Proud to be sustainable: Upcycled versus recycled luxury products. J. Bus. Res. 2021, 130, 137–146. [Google Scholar] [CrossRef]
  63. Gregory-Smith, D.; Smith, A.; Winklhofer, H. Emotions and dissonance in “ethical” consumption choices. J. Mark. Manag. 2013, 29, 1201–1223. [Google Scholar] [CrossRef] [Green Version]
  64. Zeng, T.; Durif, F. The influence of consumers’ perceived risks towards eco-design packaging upon the purchasing decision process: An exploratory study. Sustainability 2019, 11, 6131. [Google Scholar] [CrossRef] [Green Version]
  65. De Groot, J.I.M.; Steg, L. Morality and nuclear energy: Perceptions of risks and benefits, personal norms, and willingness to take action related to nuclear energy. Risk Anal. 2010, 30, 1363–1373. [Google Scholar] [CrossRef]
  66. Schwartz, S.H. Universals in the content and structure of values: Theoretical advances and empirical tests in 20 countries. Adv. Exp. Soc. Psychol. 1992, 25, 1–65. [Google Scholar] [CrossRef]
  67. Dunlap, R.E.; Van Liere, K.D. The “new environmental paradigm”. J. Environ. Educ. 1978, 9, 10–19. [Google Scholar] [CrossRef]
  68. Ibtissem, M.H. Application of value beliefs norms theory to the energy conservation behaviour. J. Sustain. Dev. 2010, 3, 129–139. [Google Scholar] [CrossRef]
  69. Wang, Y.; Hazen, B.T.; Mollenkopf, D.A. Consumer value considerations and adoption of remanufactured products in closed-loop supply chains. Ind. Manag. Data Syst. 2018, 118, 480–498. [Google Scholar] [CrossRef]
  70. Lee, J.; Lee, J.N. Understanding the product information inference process in electronic word-of-mouth: An objectivity-subjectivity dichotomy perspective. Inf. Manag. 2009, 46, 302–311. [Google Scholar] [CrossRef]
  71. Couper, M.P. Web surveys: A review of issues and approaches. Public Opin. Q. 2000, 64, 464–494. [Google Scholar] [CrossRef]
  72. Ringle, C.M.; Wende, S.; Becker, J.M. SmartPLS 3. 2015. Available online: https://www.smartpls.com (accessed on 24 January 2022).
  73. Hair, J.F.; Sarstedt, M.; Ringle, C.M.; Gudergan, S.P. Advanced Issues in Partial Least Squares Structural Equation Modeling; SAGE Publications: Thousand Oaks, CA, USA, 2018. [Google Scholar]
  74. Kock, N.; Hadaya, P. Minimum sample size estimation in PLS-SEM: The inverse square root and gamma-exponential methods. Inf. Syst. J. 2018, 28, 227–261. [Google Scholar] [CrossRef]
  75. Hair, J.F.; Sarstedt, M.; Hopkins, L.; Kuppelwieser, V.G. Partial least squares structural equation modeling (PLS-SEM): An emerging tool in business research. Eur. Bus. Rev. 2014, 26, 106–121. [Google Scholar] [CrossRef]
  76. Richter, N.F.; Sinkovics, R.R.; Ringle, C.M.; Schlägel, C. A critical look at the use of SEM in international business research. Int. Mark. Rev. 2016, 33, 376–404. [Google Scholar] [CrossRef]
  77. Hair, J.F.; Black, W.C.; Babin, B.J.; Anderson, R.E. Multivariate Data Analysis, 7th ed.; Prentice Hall: Upper Saddle River, NJ, USA, 2010. [Google Scholar]
  78. Fornell, C.; Larcker, D.F. Evaluating structural equation models with unobservable variables and measurement error. J. Mark. Res. 1981, 18, 39–50. [Google Scholar] [CrossRef]
  79. Henseler, J.; Ringle, C.M.; Sarstedt, M. A new criterion for assessing discriminant validity in variance-based structural equation modeling. J. Acad. Mark. Sci. 2015, 43, 115–135. [Google Scholar] [CrossRef] [Green Version]
  80. Kock, N. Common method bias in PLS-SEM: A full collinearity assessment approach. Int. J. e-Collab. 2015, 11, 1–10. [Google Scholar] [CrossRef] [Green Version]
  81. Kenny, D.A. Moderator Variables: Effect Size and Power. 2015. Available online: http://davidakenny.net/cm/moderation.htm (accessed on 24 January 2022).
  82. Becker, T.E. Potential problems in the statistical control of variables in organizational research: A qualitative analysis with recommendations. Organ. Res. Methods 2005, 8, 274–289. [Google Scholar] [CrossRef]
  83. Grimm, P. Social desirability bias. Wiley Int. Enc. Market. 2010. [Google Scholar] [CrossRef]
  84. Crowne, D.P.; Marlowe, D. A new scale of social desirability independent of psychopathology. J. Consult. Psychol. 1960, 24, 349. [Google Scholar] [CrossRef] [Green Version]
  85. Strahan, R.; Gerbasi, K.C. Short, homogeneous versions of the Marlowe-Crowne social desirability scale. J. Clin. Psychol. 1972, 28, 191–193. [Google Scholar] [CrossRef]
  86. Kaiser, F.G.; Hubner, G.; Bogner, F.X. Contrasting the theory of planned behavior with the value-belief-norm model in explaining conservation behavior. J. Appl. Soc. Psychol. 2005, 35, 2150–2170. [Google Scholar] [CrossRef]
  87. Roselius, T. Consumer rankings of risk reduction methods. J. Mark. 1971, 35, 56–61. [Google Scholar] [CrossRef]
  88. Lee, D.N.; Hutchens, M.J.; Krieger, J.L. Resolving the do/do dot debate communication perspective to enhance sustainable lifestyles. Sustainability 2022, 14, 796. [Google Scholar] [CrossRef]
  89. White, K.; MacDonnell, R.; Dahl, D.W. It’s the mind-Set that matters: The role of construal level and message framing in influencing consumer efficacy and conservation behaviors. J. Mark. Res. 2011, 48, 472–485. [Google Scholar] [CrossRef] [Green Version]
  90. Li, Y.; Yang, D.; Liu, Y. The effect of message framing on consumers’ intentions to purchase recycling-aiding products in China. Sustainability 2021, 13, 6966. [Google Scholar] [CrossRef]
Figure 1. Conceptual VBN Model for Recycled Product Purchase Intention.
Figure 1. Conceptual VBN Model for Recycled Product Purchase Intention.
Sustainability 14 03877 g001
Table 1. Studies on factors influencing recycled product purchase intention.
Table 1. Studies on factors influencing recycled product purchase intention.
No.Author(s) SampleData
Collection
Product TypeDependent Variable(s)Independent
Variable(s)
Influence
1[21]N = 312Online
Survey
Recycled products
in general
Purchase Intention
  • Positive image
+
  • Perceived product safety
+
  • Perceived quality
n.s.
  • Sustainability or environmental benefits
n.s.
2[22]N = 497Online
Survey
Recycled clothingPurchase Intention
  • Environmental concern
+
  • Personal norms
+
  • Perceived value
+
  • Willingness to pay a premium price
+
3[23]N = 16Qualitative InterviewsAthletic apparel made of recycled polyesterPurchase Intention
  • Functional value
+
  • Social value
+
  • Emotional value
+
  • Conditional value
+
  • Epistemic value
+
4[4]N = 49Online
Survey
New vs. recycled: Paper, single use camera, toner
cartridge, tire, auto parts, cell phone, printer/fax
Willingness to Pay
  • Functional risk
5[24]N = 495Online
Survey
rPET bottle-based apparelPurchase Intention
  • Quality
+
  • Image
n.s.
  • Safety
+
  • Sustainability
+
6[25]N = 258Online
Survey
Products made of recycled ocean plasticPurchase Intention
  • Anticipated conscience
+
  • Value for money
+
  • Perceived functionality
+
  • Risk of contamination
7[26]N = 425Online
Survey
Fashion products made of recycled plastic wastePurchase Intention
  • Product quality
+
  • Community influence
+
  • Price
8[27]N = 217Online
Survey
Recycled clothingPurchase Intention
  • Utilitarian value
+
  • Subject norms
+
  • Perceived consumer effectiveness
+
  • Environmental concern
+
9[3]N = 2400Online
Survey
Circular productsWillingness to Pay
  • Information on environmental benefits
+
  • Third-party verification
+
10[28]N = 422Online
Survey
Recycled PET productsPurchase Intention
  • Perceived quality
  • Image
+
  • Sustainability
+
  • Safety
11[29]N = 215Online
Survey
Recycled paper, mobile phones and printers.Purchase Intention
  • Attitude toward environmental protection
+
  • Perceived quality
+
+ positive Influence, − negative Influence, n.s. not significant.
Table 2. Types of Perceived Risk in Recycled Products.
Table 2. Types of Perceived Risk in Recycled Products.
Six Types of RisksDefinitions [50]Recycled Product ContextDerived from
SocialRisk that the purchase will negatively affect the
perceptions of others about the consumer
  • Peers could have unspoken, negative associations with recycled products
  • Unwanted “eco-freak” image
  • It is difficult to keep up with current trends because recycled products have a longer life cycle, e.g., fashion products
[52]
FinancialRisk that the product will not be the best possible monetary gain for the consumer
  • Recycled products are more expensive
  • Perceived risk that recycled products must be repaired more often and thus requires more repair costs
  • Worse perceived value for money, because it is not “new”
[53,54,55]
PhysicalRisk that the product will
result in health problems for the consumer
  • Risk of chemicals e.g., in counterfeit products
  • Processing of materials is not so well explored, e.g., backpack out of truck tarpaulin that was previously polluted
  • Bad surface feel, e.g., recycled toilet paper
[56,57]
PerformanceRisk that the product will not function to the satisfaction of the consumer
  • Recycled products are perceived to have a lower quality, break faster and have a weaker performance
  • Less knowledge about processes and effort, worse communication
  • Recycled products often look different than conventional products, not what consumers are familiar with or want
[58,59]
Time-RelatedRisk that the consumer will waste time or lose
convenience
  • Product availability: Fewer choice options, it involves more time to find the right product
  • Limited variety in recycled products, e.g., not the wanted color, etc.
  • Information search, potentially greenwashing
  • Longer drive to a store that has the recycled product alternative
[58,60,61]
PsychologicalRisk that the product will have a negative effect on the consumers’ peace of mind or self-perception
  • Feeling of “disgust or contamination”, e.g., when wearing recycled clothes
  • Worry or regret that the product was not the right choice
[62,63]
Table 3. Construct Scales and Validity.
Table 3. Construct Scales and Validity.
ConstructItems (Reflective Measures)Factor LoadingsSig.
(t-Value)
αAVECR
Biospheric Values
(adapted from [33])
  • Preventing pollution
0.91240.2610.9010.8350.938
  • Respecting the earth
0.86823.613
  • Protecting the environment
0.96095.511
Altruistic
Values
(adapted from [33])
  • Social justice
0.85021.6250.7970.7050.877
  • Helpful
0.77810.760
  • Equality
0.88828.710
Environmental
Concern (adapted from [11])
  • The so-called “ecological crisis” facing humankind has been greatly exaggerated (R)
0.84029.2830.7470.6650.856
  • If things continue on their present course, we will soon experience a major ecological catastrophe
0.84528.636
  • Humans are severely abusing the environment
0.75915.951
Awareness of Consequences (adapted from [32,68])
  • Environmental pollution is a problem for society
0.77120.6540.7970.5490.859
  • The continued increase in environmental pollution is a problem
0.78018.252
  • Buying sustainable products will be advantageous for our country
0.71413.825
  • The quality of the environment will improve if more sustainable products will be bough
0.70711.418
  • Environmental pollution is a serious problem that affects me personally
0.72914.335
Ascription of Responsibility (adapted from [68])
  • I am jointly responsible for environmental pollution
0.85731.6380.8450.6840.896
  • I feel jointly responsible for the increase in environmental pollution
0.88139.528
  • I feel jointly responsible for the death of marine animals because of garbage
0.80022.539
  • Not only the government and industry are responsible for environmental pollution, but me too
0.76516.329
Personal Norms
(adapted from [68])
  • I feel morally obliged to buy recycled products, regardless of what others do
0.88139.8750.8710.7200.911
  • People like me should always buy the recycled version of a product
0.87544.442
  • I feel guilty when I do not buy recycled products
0.76416.852
  • If I would buy a new product, I would feel morally obliged to buy the recycled version of the product
0.86835.596
Perceived Risk
(adapted from [69])
  • I am afraid that the safety of recycled products is not as good as that of new products, so it may present safety risks
0.83122.1220.8880.7470.922
  • I am afraid that recycled products do not function as well as new products
0.90154.005
  • I am afraid that buying recycled products is not a good investment
0.85936.831
  • I am afraid that recycled products do not last as long as new products
0.86635.647
Purchase Intention
(adapted from [70])
  • I am positive towards buying recycled product
0.87523.1070.8590.7800.914
  • I have the intention of buying recycled products
0.90965.798
  • I think it is a good idea to buy recycled product
0.86435.811
Note: α = Cronbach’s Alpha; CR = Composite Reliability; AVE = Average Variance Extracted.
Table 4. Descriptive Statistics and Discriminant Validity (HTMT-ratio).
Table 4. Descriptive Statistics and Discriminant Validity (HTMT-ratio).
MeanStandard DeviationBVAVECACARPNRiskIntent
BV4.350.81
AV4.210.780.632
EC4.060.870.4050.456
AC4.100.650.4710.4670.730
AR3.610.870.2010.2610.5470.578
PN3.000.960.2770.4100.4670.5520.396
Risk2.511.020.2280.1460.2990.5770.1590.320
Intent3.990.800.3630.3880.5400.7080.3330.6630.653
BV = Biospheric Value; AV = Altruistic Value; EC = Environmental Concern; AC = Awareness of Consequences; AR = Ascription of Responsibility; PN = Personal Norms; Risk = Perceived Risk; Intent = Purchase Intention.
Table 5. Results of the Structural Analysis.
Table 5. Results of the Structural Analysis.
Direct EffectBetaBCCI (2.5–97.5%)MeanStandard Errort-Valuep-Valuef2
H1aBV → EC0.197[0.011, 0.392]0.2080.0982.0110.0440.033
H1bAV → EC0.269[0.078, 0.432]0.2710.0912.9470.0030.062
H2EC → AC0.570[0.434, 0.675]0.5750.0619.2750.0000.481
H3AC → AR0.493[0.316, 0.623]0.4980.0766.5110.0000.321
H4AR → PN0.346[0.154, 0.503]0.3500.0883.9290.0000.136
H5PN → Intent0.455[0.353, 0.548]0.4510.0509.1050.0000.410
H6Risk → Intent−0.427[−0.513, −0.329]−0.4280.0479.1050.0000.361
Moderation EffectBetaBCCI (2.5–97.5%)MeanStandard Errort-Valuep-Valuef2
H7PN * Risk → Intent0.098[−0.150, 0.166]0.1060.0521.8990.0580.025
Control VariablesBetaBCCI (2.5–97.5%)MeanStandard Errort-Valuep-Valuef2
Gender → Intent−0.000[−0.101, 0.099]0.0010.0520.0030.9970.000
Age → Intent0.059[−0.035, 0.152]0.0610.0481.2410.2150.008
SD → Intent0.034[−0.061, 0.133]0.0300.0500.6690.5030.002
AV = Altruistic Value; BV = Biospheric Value; EC = Environmental Concern; AC = Awareness of Consequences; AR = Ascription of Responsibility; PN = Personal Norms; Risk = Perceived Risk; Intent = Purchase Intention; SD = Social Desirability.
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Hein, N. Factors Influencing the Purchase Intention for Recycled Products: Integrating Perceived Risk into Value-Belief-Norm Theory. Sustainability 2022, 14, 3877. https://doi.org/10.3390/su14073877

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Hein N. Factors Influencing the Purchase Intention for Recycled Products: Integrating Perceived Risk into Value-Belief-Norm Theory. Sustainability. 2022; 14(7):3877. https://doi.org/10.3390/su14073877

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Hein, Nika. 2022. "Factors Influencing the Purchase Intention for Recycled Products: Integrating Perceived Risk into Value-Belief-Norm Theory" Sustainability 14, no. 7: 3877. https://doi.org/10.3390/su14073877

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