Purpose

The purpose of this study is to identify enablers and barriers influencing single-use plastic (SUP) milk bottle volume reduction in New Zealand using the Capability–Opportunity–Motivation–Behaviour (COM-B) theory. Single-use plastic (SUP) milk bottles contribute significantly to plastic waste, yet when compared to other types of single-use plastic packaging (e.g. plastic bags), they have received far less research attention.

Design/methodology/approach

The study conducted in-depth interviews with 20 milk consumers in New Zealand, thoroughly analyzed via reflexive thematic analysis in NVivo 14.

Findings

Findings reveals key drivers of change, including heightened awareness of plastic waste, concerns over plastic-related health risks and recognition of recycling limitations. However, significant barriers persist, such as cost constraints, the market dominance of milk plastic packaging, limited reusable milk alternatives and insufficient policy support. Many participants indicated that high prices and low availability of reusable milk options impede broader adoption.

Practical implications

By applying the COM-B model, the study offers deeper insights into how individual and systemic factors intersect, revealing key strategic guidance for policymakers, producers, retailers and environmental advocates seeking to transform the dairy supply chain for circular economy objectives. This study emphasizes the need for holistic, multi-level interventions, policy development, enhanced retail infrastructure and behaviour change, to foster a shift toward sustainable and cost-effective sustainable packaging.

Originality/value

This is the first study to explore consumers’ barriers and enablers to reduce milk plastic packaging. The findings of this study add to the existing literature on plastic reduction and behaviour change.

The rise in single-use plastic (SUP) packaging is alarming. For instance, approximately 500 billion plastic bags are used worldwide each year, equating to over 1 million bags every minute, each lasting only 15 min (Plastic Oceans, 2023). Additionally, 15,000 plastic bottles are sold per second globally, totalling 480 billion annually, with Coca-Cola selling 110 billion bottles each year (Plastic Soup Foundation, 2023). This surge in SUP consumption has resulted in significant waste and pollution, with severe environmental and health consequences. Since the 1950s, 8.3 billion metric tons of SUP have been produced, with 6.3 billion metric tons now waste (Geyer et al., 2017). Discarded plastics also pose risks to human and animal health, leading to endocrine disruption, neurological effects, and organ damage (Cook and Halden, 2020).

Current solutions mainly focus on improving recycling systems, such as enhancing waste-sorting infrastructure and educating consumers about proper disposal (Bian et al., 2022). However, large volumes of single-use plastic continue to accumulate in landfills and ecosystems, causing pollution, harming health, and endangering wildlife (Dey et al., 2021). For example, nearly 48,000 tonnes of plastic milk bottles become waste yearly, with only 5% recycled in Australia (Madden et al., 2023). This issue arises from inadequate waste management and high demand for SUP packaging, which is cheaper and lighter than reusable alternatives (Heidbreder et al., 2019; Van Hau, 2024). Therefore, addressing SUP consumption at its source is crucial for achieving long-term environmental and health benefits.

Two main approaches are commonly employed to reduce single-use plastic (SUP) consumption: individual-level (I-level) interventions and system-level (S-level) interventions (Chater and Loewenstein, 2022; Connolly et al., 2024). I-level interventions focus on altering individual consumers’ behaviours and cognitions through education, information, or other behaviour-change techniques (Heidbreder et al., 2019), and they are frequently used by behavioural scientists (Chater and Loewenstein, 2022). However, these interventions often address SUP consumption in general, ignoring the distinct ways in which consumers use specific plastic products (e.g. bottles vs. bags) in various contexts (Heidbreder et al., 2021; Mathew et al., 2024). While they show short-term success (Truelove et al., 2023), their effectiveness declines without continued funding (Loschelder et al., 2019), thereby reducing their long-term impact on SUP consumption.

S-level interventions, on the other hand, aim to restructure the choice environment itself, thereby influencing consumer decisions more directly and specifically (Chater and Loewenstein, 2022). These interventions typically employ regulatory measures (e.g. bans) (Jehangir et al., 2022) or economic instruments (e.g. taxes, levies, deposit-refund schemes) (Martinho et al., 2017), frequently employed by policymakers (Chater and Loewenstein, 2022) if policy initiatives are supported by members of the public. Policy changes can be implemented at the macro level (e.g. country or regional) or the meso level (e.g. communities, cafés, supermarkets, or local shops) by limiting or removing SUP options (Bharadwaj et al., 2021). However, S-level interventions typically focus on a limited range of items, with SUP bags being the most common target, while other prevalent SUP forms, such as milk bottles, are often overlooked (Allison et al., 2022; Borg et al., 2022). This narrow focus can lead to substitution effects, where consumers shift from banned or taxed items to other SUP products (Jehangir et al., 2022; Macintosh et al., 2020). Furthermore, the effectiveness of S-level policies heavily depends on enforcement. In areas with weaker oversight, like farmer’s markets or smaller shops, SUP consumption often remains unaffected, diminishing the potential impact of these interventions (Bharadwaj et al., 2023; Frey and Cifuentes, 2024).

Moving toward reusable non-plastic alternatives is crucial in reducing the environmental impact of single-use plastics (SUP). Reusable non-plastics, like glass, metal, or fabric, can be used multiple times, reducing the need for disposable plastic products. Recyclable plastics face challenges with contamination, sorting, and collection, limiting their effectiveness. Reusable non-plastic systems reduce plastic waste and encourage sustainable habits when designed well and accessible (Heidbreder et al., 2021). However, effective implementation requires support at both the individual (I-level) and systemic (S-level) levels (Andreas and Jabakhanji, 2023) because individual behaviours alone may not be sufficient without the structural support of policies, infrastructure, and incentives that promote sustainable practices.

Milk is consumed by an estimated 6 billion people worldwide (Food and Agriculture Organization, 2023), reflecting its status as a dietary staple across diverse cultures. Currently, there is heavy reliance on single-use plastic (SUP) bottles for milk packaging due to their convenience and cost-effectiveness for both consumers and producers (Błażejewski et al., 2021). In 2023, global dairy production reached over 950 million metric tons (Food and Agriculture Organization, 2024); if packaged in 2-L plastic bottles, over 19 million tons of bottles would be used annually. This increased production and consumption of SUP milk bottles creates significant environmental issues, including pollution, resource depletion, and carbon emissions from production and disposal.

New Zealand faces both economic opportunities and ecological challenges from large-scale dairy production. As one of the world’s largest dairy exporters, it supplies nearly 30% of internationally traded dairy products, generating NZD 18.6 billion in export revenue in 2021 (Dairy Companies Association of New Zealand, 2023). Domestic consumption is also high, with around 535 thousand metric tons of milk consumed annually (Granwal, 2024). Yet this strong demand feeds into a substantial volume of SUP waste: each year, around 23,000 tonnes of plastic milk bottles are discarded in New Zealand, a large proportion of which are neither recycled nor reused effectively (Roden, 2024; WasteMINZ, 2020). Most bottles end up in landfills (Farrelly and Green, 2020) or are exported to non-OECD countries (e.g. Malaysia, Indonesia, and Vietnam), where contaminated plastics are often burned (Farrelly and Chitaka, 2023). While SUP bottles dominate New Zealand’s milk-packaging market, several alternatives exist in smaller segments (Table 1) (Food and Agriculture Organization, 2023; WasteMINZ, 2020).

Table 1

Overview of milk packaging alternatives in the New Zealand market

Packaging typeCommon sizesApprox. Market share (%)Example New Zealand brandsSustainability notes
HDPE plastic bottle (single use)1 L, 2 L, 3 L∼85 to 90Anchor, Meadow FreshRecyclable but single use; major waste source
Paperboard carton (Tetra pak)500 mL, 1 L, 2 L∼8 to 10So Good, Meadow Fresh CalciLower plastic content but limited recycling
Returnable glass bottle1 L∼1 to 2Lewis Road Creamery, Otago MilkReusable and recyclable; limited distribution
Refill stationVaries<1Local dairiesHigh sustainability potential; small-scale
Source(s): Authors’ own work

These practices highlight the limitations of current supply chains and recycling efforts, reinforcing the urgency to reduce SUP milk-bottle consumption. While recycling initiatives are often promoted, achieving meaningful circularity requires eliminating single-use plastics from the system (Mathew et al., 2023; Van Hau, 2024). Glass bottles and refill systems offer promising reusable alternatives, yet previous life-cycle assessments have shown that glass bottles can generate higher environmental impacts than both plastic and carton packaging for perishable liquids (Brock and Williams, 2020; Stefanini et al., 2021). More recently, Nilsson et al. (2024) reviewed evidence on reusable milk packaging and found limited support for environmental or safety advantages compared with recycling alternatives. Together, these studies underline the need for a balanced, evidence-based understanding of the trade-offs among packaging materials. To the best of current knowledge, most efforts have focused on improving recycling rather than developing robust “reduce and reuse” models. This study aims to set an agenda for advancing both individual- and system-level solutions to reduce SUP milk bottles in New Zealand.

Existing interventions to reduce single-use plastics (SUP) often use individual-level (i-level) or system-level (s-level) approaches to drive behaviour change. However, many efforts focus on measuring behaviour changes without analyzing underlying behavioural and attitudinal mechanisms, making it difficult to determine effective elements. As a result, i-level interventions are often temporary, while s-level tactics (e.g. bans or taxes) rely on strict enforcement. A more robust use of theory could address these issues. Evidence shows that interventions are most successful and enduring when grounded in strong theoretical frameworks (Michie et al., 2018; Rundle-Thiele et al., 2019). A solid theoretical grounding is fundamental to any effective behaviour change intervention. As Brennan et al. (2014) noted, “if the theoretical input is either incorrect, of low quality, or irrelevant to the problem at hand, the result will be ineffective regardless of the quality of the intervention” (p. 331). Indeed, interventions underpinned by appropriate theoretically-driven behaviour change models are more successful and lead to longer-lasting changes (Michie and Abraham, 2004).

Current efforts to reduce SUP packaging typically employ cognitive theories—where individuals use reason and information to make optimal choices—or conative theories, which view decisions as rooted in prior experiences and social environments (Brennan et al., 2014). Many SUP reduction interventions adopt the Theory of Planned Behaviour (TPB) (Ajzen, 1991), focussing on perceived behavioural control, subjective norms, and intention (Heidbreder and Schmitt, 2020; Heidbreder et al., 2020; Truelove et al., 2023). However, TPB predictors were found to be effective only in the initial adoption phase, with little impact on sustained behaviour (Heidbreder and Schmitt, 2020). Similarly, Heidbreder et al. (2020) found that rational choice models worked mainly for participants with low pro-environmental identities. Bertossi et al. (2024) perceived environmental benefits appear to influence purchase intention only for plastic and paper single-use cups, whereas perceived contamination risk affects only the reusable cup. These findings suggest that relying solely on individual psychological models may overlook the complexity of human behaviour (Rundle-Thiele et al., 2019), including factors related to “consumer myopia” (Brennan et al., 2016).

Conative models, such as the Nudge theory (Thaler and Sunstein, 2009), are frequently employed to alter the choice environment so consumers are prompted to change their behaviour (Homonoff, 2018; Mundt et al., 2020). Mundt et al. (2020) found that nudges facilitate behaviour shifts without educating consumers on why changes are necessary, undermining the development of lasting habits. For example, banning SUP bags may reduce their use but lead to increased consumption of other plastic products, such as bin liners and produce bags (Frey and Cifuentes, 2024; Macintosh et al., 2020). Psychological insights are needed to help consumers understand the rationale behind these changes, improving sustained adoption (Rundle-Thiele et al., 2021). Many of the theories mentioned overlook the complexity of adopting a systems approach (Rundle-Thiele et al., 2019), leading to an intention-behaviour gap (ElHaffar et al., 2020). This suggests that a comprehensive model addressing both individual and system aspects should be applied to SUP reduction.

The Capability–Opportunity–Motivation–Behaviour (COM-B) theory offers a valuable framework for identifying the individual, sociocultural, and situational factors that influence behaviour (Michie et al., 2011), combining both conative and cognitive models. According to the model, individuals must have both the physical and psychological ability (C), sufficient opportunity (O), and adequate motivation (M) to perform a given behaviour (B) at any moment (Michie et al., 2014). In the COM-B model, capability refers to an individual’s knowledge, skills, and abilities to engage in a particular behaviour in COM-B, which encompasses psychological capability (mental state and level of knowledge), and physical capability. Opportunity encompasses external factors facilitating behaviour execution, including physical and social opportunities. Motivation refers to the internal processes that impact decision-making and behaviour. The two primary components of motivation are extrinsic motivation, driven by external rewards or pressures, and intrinsic motivation, driven by personal interest, enjoyment, or internal satisfaction. Previous research and use of the COM-B framework have effectively identified perceived barriers linked to the capability, opportunity, and motivation components (Allison et al., 2021). In addition, COM-B has supported the creation of integrated marketing campaigns designed to promote behavioural change (Manika et al., 2022). Therefore, this theoretical perspective for a behavioural diagnosis pinpoints the COM-B elements that inform design interventions.

The COM-B model has also been used in other relevant pro-environmental literature, for instance, reducing food waste (Manika et al., 2022) and encouraging recycling behaviours (Roy et al., 2022), while its application in the domain of curbing plastic packaging use remains relatively scarce (Mathew et al., 2023). This exploratory study addresses that gap by leveraging the COM-B model to investigate the capabilities, opportunities, and motivations that shape the reduction of single-use plastic (SUP) milk bottle consumption among New Zealand residents who, at the time of data collection, were partially reducing their SUP dependence or had not yet adopted any reduction strategies. Drawing on existing SUP reduction literature and the COM-B framework, this research further illuminates the barriers and facilitators to change and provides actionable insights for designing interventions. Consequently, the following research questions (RQs) were identified to guide the study:

RQ1.

What are the key enablers encouraging consumers to reduce their consumption of single-use plastic (SUP) milk bottles?

RQ2.

What are the key barriers discouraging consumers to reduce their consumption of single-use plastic (SUP) milk bottles?

This study employed an interpretive approach to explore the drivers and barriers to reducing the reliance on SUP milk bottles. In-depth interviews were used to test the COM-B theory in the context of reducing SUP milk packaging in New Zealand. Qualitative research design offers a thorough exploration of complex phenomena (Saunders et al., 2019). Qualitative approaches, such as in-depth interviews, can capture insights into consumers’ perspectives that might be overlooked by alternative research methods, especially the topics that have not been explored before (e.g. plastic milk bottles).

Purposive sampling was used to recruit participants with substantial knowledge of the research topic (Creswell and Clark, 2018; Saunders et al., 2019). Eligible participants were consumers who had reduced their use of single-use plastic (SUP) milk bottles, intended to do so or had contemplated doing so and consumed milk at least once a week. All participants were over 18 and resided in New Zealand. A brief screening questionnaire was distributed to confirm interview eligibility.

A total of 25 participants were recruited through advertisements in three New Zealand cities (Dunedin, Auckland, and Wellington) and via social media platforms, including the authors’ personal and professional networks. Five individuals were excluded for the following reasons: (1) they did not consume milk at all, or (2) they purchased only 1 litre of milk per month. The remaining 20 eligible participants were invited to an interview, with informed consent obtained via email before scheduling.

Appendix 1 in the Supplementary file presents the demographic details of the eligible participants. In total, the sample comprised 20 participants (n = 20): 16 females (80%) and 4 males (20%), aged 21–64 years, with 9 (45%) above 40, 5 (25%) above 50, and 4 (20%) above 60. Twelve participants (60%) resided in family households, while 8 (40%) lived in flatshares. Weekly milk consumption varied from 500 mL to 10 L, with 12 participants (60%) reporting 2 L/week or more, equating to 2–3 plastic bottles per week.

All interviews were conducted between 30 August 2024 and 2 October 2024 using Zoom or Microsoft Teams and lasted approximately 20–75 min. During the interviews, participants answered questions about their capabilities, motivation, and opportunities to participate in SUP reduction following the interview protocol (see Appendix 2, Supplementary file). The interview guide was developed by existing research on behaviour change, specifically drawing on the COM-B framework (Manika et al., 2022; Roy et al., 2022).

All interviews were audio-recorded to accurately transcribe data, ensuring precise capture of participants’ responses by the lead author. The recordings were transcribed verbatim, excluding non-verbal cues (e.g. pauses, laughter), and personal identifiers were removed to maintain confidentiality. Transcripts were imported into NVivo 14 for analysis.

Data analysis was conducted using reflexive thematic analysis step by step (Braun and Clarke, 2006), following a deductive approach informed by the COM-B model (Michie et al., 2011) (see Appendix 3 in Supplementary file). A preliminary coding book (see Appendix 4 in Supplementary file) was developed using the COM-B categories—capabilities, opportunities, and motivation. The transcripts were coded to reduce single-use plastic (SUP) milk bottles, with sub-categories created inductively within each category. For instance, under the “capabilities” category (barriers), subcodes were created for “Practicality and Durability of Plastic” and “Required skills in using reusable glass bottles” (see Appendix 5 in Supplementary file for details of codes and themes).

These codes were mapped into themes, as summarized in Figure 1. The first researcher coded all transcripts and proposed an initial set of themes; another researcher independently coded 25% of the transcripts (Cohen’s kappa = 0.83). The research team collectively reviewed and refined the themes to ensure consistency and accuracy.

Figure 1
A figure shows barriers and enablers mapped across capability, opportunity, and motivation for reducing single-use plastic milk bottles.The figure contains two vertical columns of text boxes labeled “Barriers” at the top left and “Enablers” at the top right. These are connected across three horizontal levels by text boxes positioned at the center, labeled “Capability (C)”, “Opportunity (O)”, and “Motivation (M)”. Each central level is connected by solid horizontal lines to both the barrier and enabler text boxes. Under the Capability (C) level, the barriers list includes “Practicality and durability of plastic (C B 1)” and “Required skills in using reusable glass bottles (C B 2)”. Under the same Capability (C) level, the enablers list includes “Awareness of plastic waste problem (C E 1)”, “Complexities of proper recycling practices (C E 2)”, “Awareness of downcycling limitations (C E 3)”, “Growing recognition of glass as a functional and sustainable alternative (C E 4)”, and “Awareness of milk in plastic linked to food waste (C E 5)”. Under the Opportunity (O) level, the barriers list includes “Limited access to reusable packaging options (O B 1)”, “The dominance of plastic packaging in the market (O B 2)”, “Perceived limitation of current reusable systems (O B 3)”, “Lack of consumer awareness and education (O B 4)”, “Insufficient policy and regulatory support (O B 5)”, “The absence of milk delivery services or refill stations (O B 6)”, and “Lack of diverse options in reusable alternatives (O B 7)”. Under the same Opportunity (O) level, the enablers list includes “Cultural shift towards sustainability (O E)”. Under the Motivation (M) level, the barriers list includes “Affordability of plastic bottles (M B 1)” and “Convenience of plastic bottles (M B 2)”. Under the same Motivation (M) level, the enablers list includes “Growing preferences for the quality and taste of glass-bottled milk (M E 1)”, “Concern about health and safety of plastic (M E 2)”, “Support for small and local businesses (M E 3)”, and “Growing commitment to developing sustainable non-plastic habits (M E 4)”.

Summary of themes from interviews organized through the COM-B model. Source: Authors’ own work

Figure 1
A figure shows barriers and enablers mapped across capability, opportunity, and motivation for reducing single-use plastic milk bottles.The figure contains two vertical columns of text boxes labeled “Barriers” at the top left and “Enablers” at the top right. These are connected across three horizontal levels by text boxes positioned at the center, labeled “Capability (C)”, “Opportunity (O)”, and “Motivation (M)”. Each central level is connected by solid horizontal lines to both the barrier and enabler text boxes. Under the Capability (C) level, the barriers list includes “Practicality and durability of plastic (C B 1)” and “Required skills in using reusable glass bottles (C B 2)”. Under the same Capability (C) level, the enablers list includes “Awareness of plastic waste problem (C E 1)”, “Complexities of proper recycling practices (C E 2)”, “Awareness of downcycling limitations (C E 3)”, “Growing recognition of glass as a functional and sustainable alternative (C E 4)”, and “Awareness of milk in plastic linked to food waste (C E 5)”. Under the Opportunity (O) level, the barriers list includes “Limited access to reusable packaging options (O B 1)”, “The dominance of plastic packaging in the market (O B 2)”, “Perceived limitation of current reusable systems (O B 3)”, “Lack of consumer awareness and education (O B 4)”, “Insufficient policy and regulatory support (O B 5)”, “The absence of milk delivery services or refill stations (O B 6)”, and “Lack of diverse options in reusable alternatives (O B 7)”. Under the same Opportunity (O) level, the enablers list includes “Cultural shift towards sustainability (O E)”. Under the Motivation (M) level, the barriers list includes “Affordability of plastic bottles (M B 1)” and “Convenience of plastic bottles (M B 2)”. Under the same Motivation (M) level, the enablers list includes “Growing preferences for the quality and taste of glass-bottled milk (M E 1)”, “Concern about health and safety of plastic (M E 2)”, “Support for small and local businesses (M E 3)”, and “Growing commitment to developing sustainable non-plastic habits (M E 4)”.

Summary of themes from interviews organized through the COM-B model. Source: Authors’ own work

Close modal

Enablers and Barriers to reducing SUP milk bottle consumption in the New Zealand context were identified through reflexive thematic analysis. The findings are organized into barriers and enablers with respect to the capability, opportunity and motivation components of the COM-B model. Twenty-one key themes emerged from the codes, which were mapped to the COM-B model’s Capability, Opportunity, and Motivation components (as depicted in Figure 1).

4.1.1 Enablers

Capability is the factor that helps people use their knowledge, skills, or abilities to act (Section 2.2). Regarding the enablers of capability, four key themes emerged from the data. The first theme, “awareness of the plastic waste problem” (CE1), underscores that many consumers recognize how plastic waste contributes to pollution, climate change, and global warming. For instance, Participant 4 noted:

The downside of plastic is bad for the environment. It takes thousands of years to break down and ends up as bulk in landfills. That land could be used much more productively. […] When plastic waste breaks down, it releases toxic gases contributing to global warming.

The second theme, “complexities of proper recycling practices” (CE2), highlights the considerable skills and knowledge gap consumers face when properly recycling plastic. Tasks such as identifying different types of recyclable plastics, rinsing containers, and removing non-recyclable lids can be challenging. Participant 14 expressed frustration in this regard:

Recycling milk plastic bottles is frustrating because there are too many rules about cleaning the bottles and separating parts because the lids can not end up in recycling bins [1].

The third theme, “awareness of downcycling limitations” (CE3), points to participants’ understanding that plastic recycling often results in downcycling, wherein recovered plastic becomes lower-quality material unsuitable for reuse in food packaging. Participant 8 questioned the broader environmental impact of recycling:

I am not sure if the plastic gets recycled. Even though I am told it’s recycled, I wonder what it’s recycled into and what the carbon footprint of recycling is. Where is it taken? Is it shipped offshore? I once saw an advertisement that said: “We throw things away, but there is no way.”

The fourth theme, “growing recognition of glass as a functional and sustainable alternative” (CE4), arises from participants’ awareness of glass’s reusability, lack of microplastic contamination, and effectiveness in keeping milk colder and fresher for longer. The availability of milk in glass packaging reinforces consumers’ capacity to make more sustainable choices.

The last theme is “awareness of milk in plastic linked to food waste” (CE5), highlighting that milk in large plastic containers could become waste. Participant 7 highlighted how large plastic containers can lead to milk waste when the product spoils before it can be finished:

Milk comes in plastic packaging and is usually too large […] I think I am getting a cheaper deal with a large volume, but I often cannot finish it […] The spoiled milk then ends up as food and plastic waste.

4.1.2 Barriers

Regarding the barriers to capability, two key themes emerged from the data. The first theme, “practicality and durability of plastic” (CB1), highlights plastic’s capacity to remain intact under pressure and its extended shelf life, both of which make it an appealing choice for consumers prioritizing convenience and safety. Participant 11 illustrated this point:

Plastic packaging lasts longer and can withstand more pressure than alternatives, such as glass, cartons or cans. […] You don’t need to keep or store the bottles to swap for your next shopping.

The second theme, “required skills in using reusable glass bottles” (CB2), shows the logistical and cognitive challenges of adopting milk glass bottles. Consumers must remember to wash and return the bottles, which is less convenient than using single-use plastic. Participant 2 explained:

Glass bottles are an option, but the issue is that you have to bring them back to swap. […] This creates an additional burden for the consumer, who has to remember to bring the bottle. […] Also, you need a wash bottle, which adds to the inconvenience.

4.2.1 Enablers

Opportunity refers to external conditions or resources that make it easier to perform a behaviour, such as access to tools (physical opportunity) or support from others (social opportunity) (Section 2.2). In terms of enablers of opportunity, only one theme emerged from the data: “cultural shift towards sustainability” (OE). This theme captures a growing societal awareness and adoption of sustainable practices across various levels, encompassing recycling programs, school educational campaigns, and public advocacy to reduce plastic consumption. Efforts to promote alternatives to single-use plastics are increasingly coupled with emotive campaigns linking environmental issues to recognizable symbols. Participant 7 mentioned the global initiative:

I have seen Plastic-Free July by Greenpeace on social media. The idea is that individual change at scale can have a big impact. […] They promote the video and image about plastic waste harming marine wildlife.

4.2.2 Barriers

Related to barriers of opportunity, seven themes emerged from the dataset. Collectively, these themes illustrate the multifaceted challenges consumers face when transitioning from single-use plastic to more sustainable alternatives. The most prominent theme is “limited access to reusable packaging options” (OB1), highlighting the scarcity of reusable alternatives—particularly glass bottles—in mainstream retail outlets such as supermarkets. As Participant 2 described:

The major supermarkets in my area usually sell milk in plastic bottles. However, I have found that local stores or farmer’s markets offer milk in glass bottles. Unfortunately, these stores are quite far from my home and are located remotely from the city centre near the farm where the milk is produc

The second theme is “the dominance of plastic packaging in the market” (OB2), reflecting the perception of plastic as the default, most accessible choice. Participant 6 voiced a concern over the omnipresence of plastic:

The problem with plastic is that there’s a lot of propaganda and persuasive language surrounding it. [..] Plastic is still everywhere […] You just walk into the supermarket and grab it.

The third theme is the “perceived limitation of current reusable systems” (OB3), which emphasizes the logistical and practical difficulties consumers encounter when trying to use reusable bottles. Participant 20 explained:

[…] I used to get milk from the farmer’s market, but carrying multiple heavy glass bottles home was inconvenient […]

The fourth theme is “lack of consumer awareness and education” (OB4), underscoring the importance of informed consumer choices and targeted outreach. Participant 13 noted that while broader environmental campaigns exist, they seldom focus on milk:

I have not come across any specific campaigns for milk. […] The only similar efforts I have seen are for laundry products, where companies offer refills in compact containers to reduce plastic use.

The fifth theme is “insufficient policy and regulatory support” (OB5), which focuses on government measures that could facilitate the transition to sustainable milk packaging. Participant 4 observed:

Honestly, I do not see much changing because big companies like Fonterra are so powerful, and the government is not likely to take a strong stance against big businesses. […] Change should likely come from grassroots movements […]

Participant 17 suggested that price interventions and incentives could help overcome cost barriers:

Making the price of glass bottles equivalent to plastic bottles and offering glass options in more stores […] government could invest in companies making cheaper alternatives […] offer tax incentives to companies that switch to alternative packaging materials.

The sixth theme is “the absence of milk delivery services or refill stations” (OB6), drawing attention to the decline of once-widespread systems that deliver milk directly to consumers in reusable glass bottles. Participant 18 reflected on these earlier practices:

Back in the day, we had a system where you returned glass bottles with a carrier, but that’s no longer common […] we used to have milk delivered to our rural home by the postman, who would take the empty bottles and leave new ones. It was more convenient back then.

The last theme is the “lack of diverse options in reusable alternatives” (OB7), the limited range of products offered in reusable formats. Although some stores occasionally stock dairy milk in glass bottles, non-dairy and speciality milk remain largely unavailable in such formats. Participant 9 commented:

[…] I usually go for almond or other plant-based milk, but it does not exist in glass bottles […]

Participant 16 echoed this sentiment:

[…] I would love to see more non-dairy milk available in glass bottles, but I have not seen any in our major supermarkets […]

4.3.1 Enablers

Motivation—internal drivers of behaviour—includes extrinsic (external rewards/pressures) and intrinsic (personal interest/satisfaction) (Section 2.2). Four themes emerged from the data regarding enablers of motivation to reduce SUP milk bottles. The first theme is “growing preferences for the quality and taste of glass-bottled milk” (ME1), focussing on consumers’ perception that milk in glass bottles tastes better and is of higher quality. This preference is intrinsic and rooted in personal satisfaction and enjoyment. Participant 1 emphasized these benefits:

Glass looks cleaner and keeps the milk colder for longer. […] In my experience, milk in glass bottles doesn’t spoil as quickly as it does in plastic containers.

The second theme is “concern about the health and safety of plastics” (ME2), with many participants favouring glass over plastic to avoid potential chemical leaching and microplastic contamination. Participant 10 explained:

I think about safety, especially when it comes to microplastics […] I’m trying to minimize the amount of microplastic I consume.

The third theme is “support for local and small business” (ME3), reflecting participants’ desire to contribute to the local economy and support ethical, small-scale producers. Many respondents described deliberately avoiding large corporations that heavily rely on plastic. Participant 4 said:

[…] I also like supporting small and local businesses that avoid plastic packaging. Milk from them is the natural milk […]

The fourth theme is “growing commitment to developing sustainable non-plastic habits” (ME4), which captures participants’ efforts to cultivate long-term habits that reduce plastic use. Many described organizational strategies and routines to facilitate glass bottle usage. Participant 6 remarked:

I’m focused on building habits that align with my values […] I avoid plastics by always ensuring I have enough milk in the fridge. […] When I take my backpack to the car, I place the glass milk bottle beside it so I don’t forget to bring it back for refills.

4.3.2 Barriers

The first theme, “affordability of plastic bottles” (MB1), highlights how plastic packaging is often cheaper and more readily available—an essential factor for consumers on tight budgets. As Participant 20 explained:

[…] Plastic packaging is the cheapest option available […] You can buy large volumes of milk in plastic bottles for a low price, which is important for people with limited budgets […] My family consume 10 L per week, so bringing glass bottles is not a viable option.

The second theme, “convenience of plastic bottles” (MB2), reflects the lightweight, durable, and accessible nature of plastic. These attributes make it practical for consumers who prioritize ease of use and minimal breakage risk. Participant 10 offered a telling perspective:

[…] Plastic is also lighter, and if you drop it, it’s less likely to break compared to glass […] more efficient to transport than glass bottles.

This study applies the Capability-Opportunity-Motivation-Behaviour (COM-B) model to explore how single-use plastic (SUP) milk bottle consumption can be reduced. While the model’s capability, opportunity, and motivation elements help categorize factors, the results reveal its limits when system-level forces are not taken into account. Awareness of plastic’s environmental harm and recognition of glass as an alternative (capability) do little to change behaviours when market structures and habits favour plastic. These findings challenge assumptions that knowledge and good intentions alone reduce plastic consumption (Mundt et al., 2020), aligning with Otto et al. (2021), who stress that awareness and eco-labelling must be supported by structural enablers. Our findings also parallel recent evidence that effective sustainable-consumption interventions must operate across both individual (I-) and system (S-) levels (Van Hau et al., 2025a).

Opportunity factors highlight the interplay between cultural and structural elements. Societal efforts such as educational campaigns can increase consumers’ willingness to switch to alternative packaging, yet social norms alone cannot overcome the physical and economic barriers embedded in the marketplace. Limited availability of reusable options, higher upfront costs, and the dominance of plastic in supply chains exemplify how system constraints undermine even strong consumer motivation (Mathew et al., 2024; Truelove et al., 2023). Consistent with life-cycle and behavioural evidence (Brock and Williams, 2020; Nilsson et al., 2024; Stefanini et al., 2021), these results show that structural enablers must complement cultural messaging to make sustainable packaging practical and affordable.

Finally, while COM-B stresses the interplay between reflective (e.g. environmental values) and automatic (e.g. habit, convenience) motivations, our results reveal that these forces often conflict in everyday contexts. Similar to prior work on sustainable behaviour (Barkela et al., 2021; Bharadwaj et al., 2021), participants with strong environmental values frequently prioritized convenience and cost, underscoring the persistence of “friction costs” that suppress pro-environmental action. This gap between attitudes and behaviour highlights the need for behaviour-change models to incorporate the reinforcing relationship between system design and motivation, where convenience and affordability are not merely personal preferences but reflections of structural opportunity (Carrigan et al., 2023). Overall, this study extends COM-B by illustrating how the transformation of SUP habits requires coordinated changes across capability, opportunity, and motivation at both I-level and S-level, turning “green” intentions into a routine of sustainable consumption.

On a practical level, this study offers several insights that could help policymakers, retailers, and community organizations encourage consumers to reduce SUP milk bottles. Opportunity barriers highlight the need for infrastructural improvements and policy interventions. Many participants indicated they would switch to better reusable alternatives if they were more conveniently available at supermarkets or offered through affordable delivery services, supporting findings from Hallez et al. (2024). Promoting deposit-return systems, where consumers receive refunds or discounts for returning bottles, could reduce cost and inconvenience. However, viable alternatives must be cost-effective, especially for high-volume products like milk. Therefore, an S-level intervention mandating affordable reusable provision could encourage consumers to adopt reusable packaging and challenge the perception of higher costs.

This study found that motivational drivers such as better taste, aversion to microplastics, and support for small local producers encouraged behaviour change toward sustainable milk consumption. Branding and marketing that emphasize these sensory, ethical, and environmental benefits can motivate consumers to adopt more sustainable purchasing habits (Hamlin, 2016). Participants perceived reusable glass-bottled milk as fresher, healthier, and more aligned with their personal values. They also noted that buying milk in large plastic containers often led to food waste, suggesting that promoting smaller alternative sizes could help reduce both waste and plastic use. Additionally, participants noted the limited availability of plant-based milk options in reusable or refillable packaging. This presents an opportunity for producers to develop sustainable solutions that address both packaging and nutritional aspects, especially as plant-based alternatives with comparable nutritional profiles to dairy milk continue to gain global demand (Reyes-Jurado et al., 2023; Van Selm et al., 2022).

Practicality remains a key barrier, as plastic is widely perceived as cheaper, lighter, and more durable than glass (Parsons, 2022). To reduce reliance on plastic, alternative packaging must be both visible and price-competitive in the market. However, consumer perceptions of safety and freshness often reflect misconceptions rather than scientific evidence (Boesen et al., 2019; Lindh et al., 2016). For instance, while participants viewed glass bottles as safer, fresher, and more environmentally friendly, research shows that microplastics can also occur in glass and carton-based packaging (Kutralam-Muniasamy et al., 2020; Schymanski et al., 2018), and can be released from plastic caps or during cleaning processes (Winkler et al., 2019). Evidence also indicates that microplastics have been detected in milk products themselves, suggesting broader systemic contamination beyond packaging (Zhang et al., 2023). The environmental impact of glass may further be higher due to its heavier weight and energy-intensive production (Boesen et al., 2019). These findings highlight the need for clearer communication and eco-labelling to bridge the gap between consumer perception and scientific evidence. Beyond glass, retailers could explore steel containers, carton packaging, refill stations, vending machines, or milk delivery systems to promote waste reduction. However, these initiatives require retailers’ commitment to invest in infrastructure that supports sustainable supply systems. Complementary policy measures such as levies on plastic bottles, tax incentives for dairies, and phased reductions in plastic production could further stimulate industry innovation and long-term transition toward circular packaging models (Korhonen et al., 2015).

This study has several limitations, each presenting opportunities for further research. First, as it was conducted in New Zealand, future research should explore other contexts, including developing countries and different products (e.g. bottled water), to provide a broader perspective. Second, alternative methods, such as co-design, surveys, or experiments, could offer deeper insights. Third, the small sample size of 20 participants could be addressed by incorporating focus groups or co-design sessions to capture a broader range of segmentation (Van Hau et al., 2025b). Fourth, although this study applied the COM-B framework effectively, the interview guide was intentionally kept succinct to ensure participant engagement and manage time constraints. As a result, some sub-dimensions within each COM-B component were not fully explored. For instance, additional Capability questions (e.g. confidence, training, or physical ability), Opportunity prompts (e.g. specific social or policy influences), and Motivation items (e.g. goals or emotional drivers) could further enrich understanding in future research. Similarly, while Behaviour was the focal outcome in this study, future studies could explicitly operationalize and measure behavioural frequency, context, or steps to provide greater behavioural specificity. Lastly, while the study focused on plastic milk bottles, future studies could expand to other SUP types, such as straws or meat trays, especially those relevant to local contexts.

This study extends the understanding of single-use plastic (SUP) reduction by focussing on milk packaging, an overlooked yet high-impact category. Using the COM-B framework, it highlights how individual capabilities, motivations, and system-level opportunities interact to shape sustainable choices. The findings reveal that effective change requires aligning behavioural interventions with supportive infrastructure, pricing, and policy. While reusable options like glass can help, their benefits depend on local reuse rates and logistics, reinforcing the need for holistic, life-cycle-based strategies. Broader sustainability progress will depend on integrating behavioural, economic, and environmental perspectives in both policy and practice.

This research was reviewed and approved by the Human Ethics Committee, University of Otago (Reference number: 24/0396). Informed consent was obtained from participants before the commencement of the study.

1.

In New Zealand, the kerbside collection system includes three types of bins: blue bins (glass packaging), yellow bins or recycling (cans, clear plastic and cardboard), and red bins (colour plastics, contaminated plastics, soft plastics and all other types of waste). https://www.beehive.govt.nz/release/standard-kerbside-recycling-part-new-era-waste-system

The supplementary material for this article can be found online.

Ajzen
,
I.
(
1991
), “
The theory of planned behavior
”,
Organizational Behavior and Human Decision Processes
, Vol. 
50
No. 
2
, pp. 
179
-
211
, doi: .
Allison
,
Lorencatto
,
F.
,
Michie
,
S.
and
Miodownik
,
M.
(
2021
), “
Barriers and enablers to buying biodegradable and compostable plastic packaging
”,
Sustainability
, Vol. 
13
No. 
3
, p.
1463
, doi: .
Allison
,
Baird
,
H.M.
,
Lorencatto
,
F.
,
Webb
,
T.L.
and
Michie
,
S.
(
2022
), “
Reducing plastic waste: a meta-analysis of influences on behaviour and interventions
”,
Journal of Cleaner Production
, Vol. 
380
, 134860, doi: .
Andreas
,
M.
and
Jabakhanji
,
S.B.
(
2023
), “
The I-frame vs. S-frame: how neoliberalism has led behavioral sciences astray
”,
Frontiers in Psychology
, Vol. 
14
, 1247703, doi: .
Barkela
,
B.
,
Werling
,
K.
,
Filler
,
S.E.
and
Heidbreder
,
L.M.
(
2021
), “
Fasting plastic-the role of media reports in a ‘Window of Opportunity’ to reduce plastic consumption
”,
Sustainability
, Vol. 
13
No. 
21
, 11807, doi: .
Bertossi
,
A.
,
Rizzi
,
L.
,
Troiano
,
S.
and
Marangon
,
F.
(
2024
), “
Exploratory analysis of influential factors in the choices of using single-use or reusable cups in vending
”,
British Food Journal
, Vol. 
126
No. 
13
, pp. 
609
-
624
, doi: .
Bharadwaj
,
B.
,
Subedi
,
M.N.
and
Chalise
,
B.K.
(
2021
), “
Where is my reusable bag? Retailers’ bag use before and after the plastic bag ban in Dharan Municipality of Nepal
”,
Waste Management
, Vol. 
120
, pp. 
494
-
502
, doi: .
Bharadwaj
,
B.
,
Subedi
,
M.N.
and
Rai
,
R.K.
(
2023
), “
Retailer’s characteristics and compliance with the single-use plastic bag ban
”,
Sustainability Analytics and Modeling
, Vol. 
3
, 100019, doi: .
Bian
,
S.
,
Xue
,
Y.
,
Li
,
C.
,
Wu
,
W.
,
Ma
,
Z.
,
Okoro
,
J.O.
and
Harder
,
M.K.
(
2022
), “
Depositing waste in ‘certain place’ at ‘certain time’: does this policy improve recycling performance?
”,
Resources, Conservation and Recycling
, Vol. 
176
, 105935, doi: .
Błażejewski
,
T.
,
Walker
,
S.R.
,
Muazu
,
R.I.
and
Rothman
,
R.H.
(
2021
), “
Reimagining the milk supply chain: reusable vessels for bulk delivery
”,
Sustainable Production and Consumption
, Vol. 
27
, pp. 
1030
-
1046
, doi: .
Boesen
,
S.
,
Bey
,
N.
and
Niero
,
M.
(
2019
), “
Environmental sustainability of liquid food packaging: is there a gap between Danish consumers’ perception and learnings from life cycle assessment?
”,
Journal of Cleaner Production
, Vol. 
210
, pp. 
1193
-
1206
, doi: .
Borg
,
K.
,
Lennox
,
A.
,
Kaufman
,
S.
,
Tull
,
F.
,
Prime
,
R.
,
Rogers
,
L.
and
Dunstan
,
E.
(
2022
), “
Curbing plastic consumption: a review of single-use plastic behaviour change interventions
”,
Journal of Cleaner Production
, Vol. 
344
, 131077, doi: .
Braun
,
V.
and
Clarke
,
V.
(
2006
), “
Using thematic analysis in psychology
”,
Qualitative Research in Psychology
, Vol. 
3
No. 
2
, pp. 
77
-
101
, doi: .
Brennan
,
L.
,
Binney
,
W.
,
Parker
,
L.
,
Aleti
,
T.
and
Nguyen
,
D.
(
2014
),
Social Marketing and Behaviour Change
,
Edward Elgar Publishing
, doi: .
Brennan
,
L.
,
Previte
,
J.
and
Fry
,
M.L.
(
2016
), “
Social marketing’s consumer myopia applying a behavioural ecological model to address wicked problems
”,
Journal of Social Marketing
, Vol. 
6
No. 
3
, pp. 
219
-
239
, doi: .
Brock
,
A.
and
Williams
,
I.
(
2020
), “
Life cycle assessment and beverage packaging
”,
Detritus
, Vol. 
13
, pp. 
47
-
61
, doi: .
Carrigan
,
M.
,
Wells
,
V.
and
Mackay
,
K.
(
2023
), “
Transitioning beyond single-use plastic drinks cups: an emergent social marketing case study in Scotland
”,
European Journal of Marketing
, Vol. 
58
No. 
7
, pp. 
1691
-
1714
, doi: .
Chater
and
Loewenstein
(
2022
), “
The i-frame and the s-frame: how focusing on individual-level solutions has led behavioral public policy astray
”,
Behavioral and Brain Sciences
, Vol. 
46
, e147, doi: .
Connolly
,
D.J.
,
Loewenstein
,
G.
and
Chater
,
N.
(
2024
), “
An s-frame agenda for behavioral public policy research
”,
Behavioural Public Policy
, Vol. 
9
No. 
3
, pp. 
1
-
21
, doi: .
Cook
,
C.R.
and
Halden
,
R.U.
(
2020
), “Ecological and health issues of plastic waste”, in
Plastic Waste and Recycling
,
Elsevier
, pp. 
513
-
527
, doi: .
Creswell
,
J.W.
and
Clark
,
V.L.P.
(
2018
),
Research Design: Qualitative, Quantitative, and Mixed Methods Approaches
,
Sage publications
.
Dairy Companies Association of New Zealand, D.
(
2023
), “
The New Zealand dairy industry
”,
available at:
 https://dcanz.com/the-new-zealand-dairy-industry/
Dey
,
A.
,
Dhumal
,
C.V.
,
Sengupta
,
P.
,
Kumar
,
A.
,
Pramanik
,
N.K.
and
Alam
,
T.
(
2021
), “
Challenges and possible solutions to mitigate the problems of single-use plastics used for packaging food items: a review
”,
Journal of Food Science and Technology
, Vol. 
58
No. 
9
, pp. 
3251
-
3269
, doi: .
ElHaffar
,
G.
,
Durif
,
F.
and
Dubé
,
L.
(
2020
), “
Towards closing the attitude-intention-behavior gap in green consumption: a narrative review of the literature and an overview of future research directions
”,
Journal of Cleaner Production
, Vol. 
275
, 122556, doi: .
Farrelly
,
T.
and
Chitaka
,
T.Y.
(
2023
), “
Policy implications for gaps in traditional plastic waste material flow analysis: Palmerston North, New Zealand
”,
Frontiers in Sustainability
, Vol. 
4
, 982357, doi: .
Farrelly
,
T.
and
Green
,
L.
(
2020
), “
The global plastic pollution crisis: how should New Zealand respond?
”,
Policy Quarterly
, Vol. 
16
No. 
2
, doi: .
Food and Agriculture Organization, U. N
(
2023
), “
Milk and milk products
”,
available at:
 https://www.fao.org/dairy-production-products/products/milk-and-milk-products/en
Food and Agriculture Organization, U. N
(
2024
), “
FAO food outlook: dairy market highlights
”.
Frey
,
M.
and
Cifuentes
,
L.A.
(
2024
), “
Goodbye plastic bags? Lessons from the shopping plastic bag ban in Chile
”,
Sustainability
, Vol. 
16
No. 
9
, p.
3690
, doi: .
Geyer
,
R.
,
Jambeck
,
J.R.
and
Law
,
K.L.
(
2017
), “
Production, use, and fate of all plastics ever made
”,
Science Advances
, Vol. 
3
No. 
7
, e1700782, doi: .
Granwal
,
L.
(
2024
), “
Domestic consumption of milk in New Zealand from 2016 to 2023 (in 1,000 metric tons)
”,
Statista
.
Hallez
,
L.
,
Spruyt
,
B.
,
Boen
,
F.
and
Smits
,
T.
(
2024
), “
How consumers value sustainable packaging: an experimental test combining packaging material, claim and price
”,
British Food Journal
, Vol. 
126
No. 
9
, pp. 
3566
-
3583
, doi: .
Hamlin
,
R.P.
(
2016
), “
The consumer testing of food package graphic design
”,
British Food Journal
, Vol. 
118
No. 
2
, pp. 
379
-
395
, doi: .
Heidbreder
,
L.M.
and
Schmitt
,
M.
(
2020
), “
Fasting plastic: an intervention study to break habits of plastic consumption (Ayuno de plastico: una intervencion para cambiar los habitos de consumo de plasticos)
”,
Psyecology-Bilingual Journal of Environmental Psychology-Revista Bilingue De Psicologia Ambiental
, Vol. 
11
No. 
2
, pp. 
170
-
192
, doi: .
Heidbreder
,
Bablok
,
I.
,
Drews
,
S.
and
Menzel
,
C.
(
2019
), “
Tackling the plastic problem: a review on perceptions, behaviors, and interventions
”,
Science of the Total Environment
, Vol. 
668
, pp. 
1077
-
1093
, doi: .
Heidbreder
,
L.M.
,
Steinhorst
,
J.
and
Schmitt
,
M.
(
2020
), “
Plastic-free July: an experimental study of limiting and promoting factors in encouraging a reduction of single-use plastic consumption
”,
Sustainability
, Vol. 
12
No. 
11
, p.
4698
, doi: .
Heidbreder
,
L.M.
,
Lange
,
M.
and
Reese
,
G.
(
2021
), “
# PlasticFreeJuly–analyzing a worldwide campaign to reduce single-use plastic consumption with Twitter
”,
Environmental Communication
, Vol. 
15
No. 
7
, pp. 
937
-
953
, doi: .
Homonoff
,
T.A.
(
2018
), “
Can small incentives have large effects? The impact of taxes versus bonuses on disposable bag use
”,
American Economic Journal: Economic Policy
, Vol. 
10
No. 
4
, pp. 
177
-
210
, doi: .
Jehangir
,
A.
,
Imtiaz
,
M.
and
Salman
,
V.
(
2022
), “
Pakistan’s plastic bag ban: an analysis of citizens’ support and ban effectiveness in Islamabad Capital Territory
”,
Journal of Material Cycles and Waste Management
, Vol. 
24
No. 
4
, pp. 
1612
-
1622
, doi: .
Korhonen
,
V.M.
,
de La Fuente
,
J.
,
Hurley
,
R.A.
,
Guzman
,
C.
,
Cabezas
,
J.
,
González-Buesa
,
J.
,
Tanprasert
,
K.
,
Pettersen
,
M.
and
Yildirim
,
S.
(
2015
), “
Package value for the millennial generation—results of a cross-continental study
”,
Proceedings of the 27th IAPRI Symposium on Packaging
,
Valencia, Spain
.
Kutralam-Muniasamy
,
G.
,
Pérez-Guevara
,
F.
,
Elizalde-Martínez
,
I.
and
Shruti
,
V.
(
2020
), “
Branded milks–are they immune from microplastics contamination?
”,
Science of the Total Environment
, Vol. 
714
, 136823, doi: .
Lindh
,
H.
,
Olsson
,
A.
and
Williams
,
H.
(
2016
), “
Consumer perceptions of food packaging: contributing to or counteracting environmentally sustainable development?
”,
Packaging Technology and Science
, Vol. 
29
No. 
1
, pp. 
3
-
23
, doi: .
Loschelder
,
D.D.
,
Siepelmeyer
,
H.
,
Fischer
,
D.
and
Rubel
,
J.A.
(
2019
), “
Dynamic norms drive sustainable consumption: norm-based nudging helps cafe customers to avoid disposable to-go-cups
”,
Journal of Economic Psychology
, Vol. 
75
, 102146, doi: .
Macintosh
,
A.
,
Simpson
,
A.
,
Neeman
,
T.
and
Dickson
,
K.
(
2020
), “
Plastic bag bans: lessons from the Australian Capital Territory
”,
Resources, Conservation and Recycling
, Vol. 
154
, 104638, doi: .
Madden
,
B.
,
Jazbec
,
M.
and
Florin
,
N.
(
2023
), “
Increasing packaging grade recovery rates of plastic milk bottles in Australia: a material flow analysis approach
”,
Sustainable Production and Consumption
, Vol. 
37
, pp. 
65
-
77
, doi: .
Manika
,
D.
,
Iacovidou
,
E.
,
Canhoto
,
A.
,
Pei
,
E.J.
and
Mach
,
K.
(
2022
), “
Capabilities, opportunities and motivations that drive food waste disposal practices: a case study of young adults in England
”,
Journal of Cleaner Production
, Vol. 
370
, 133449, doi: .
Martinho
,
G.
,
Balaia
,
N.
and
Pires
,
A.
(
2017
), “
The Portuguese plastic carrier bag tax: the effects on consumers’ behavior
”,
Waste Management
, Vol. 
61
, pp. 
3
-
12
, doi: .
Mathew
,
Isbanner
,
S.
,
Xi
,
Y.
,
Rundle-Thiele
,
S.
,
David
,
P.
,
Li
,
G.
and
Lee
,
D.
(
2023
), “
A systematic literature review of voluntary behaviour change approaches in single use plastic reduction
”,
Journal of Environmental Management
, Vol. 
336
, 117582, doi: .
Mathew
,
A.
,
Isbanner
,
S.
and
Rundle-Thiele
,
S.
(
2024
), “
Reducing plastic waste in the workplace: a program evaluation
”,
Journal of Social Marketing
, Vol. 
14
No. 
2
, pp. 
228
-
249
, doi: .
Michie
,
S.
and
Abraham
,
C.
(
2004
), “
Interventions to change health behaviours: evidence-based or evidence-inspired?
”,
Psychology and Health
, Vol. 
19
No. 
1
, pp. 
29
-
49
, doi: .
Michie
,
S.
,
van Stralen
,
M.M.
and
West
,
R.
(
2011
), “
The behaviour change wheel: a new method for characterising and designing behaviour change interventions
”,
Implementation Science
, Vol. 
6
No. 
1
, p.
42
, doi: .
Michie
,
S.
,
Johnston
,
M.
,
West
,
R.
,
Abraham
,
C.
,
Hardeman
,
W.
and
Wood
,
C.
(
2014
), “
Designing behavior change interventions: the behaviour change wheel and behavior change techniques
”,
Annals of Behavioral Medicine
, Vol. 
47
, p.
S157
.
Michie
,
S.
,
Carey
,
R.N.
,
Johnston
,
M.
,
Rothman
,
A.J.
,
de Bruin
,
M.
,
Kelly
,
M.P.
and
Connell
,
L.E.
(
2018
), “
From theory-inspired to theory-based interventions: a protocol for developing and testing a methodology for linking behaviour change techniques to theoretical mechanisms of action
”,
Annals of Behavioral Medicine
, Vol. 
52
No. 
6
, pp. 
501
-
512
, doi: .
Mundt
,
D.
,
Carl
,
S.
and
Harhoff
,
N.
(
2020
), “
A field experiment on reducing drinking straw consumption by default
”,
Frontiers in Psychology
, Vol. 
11
, p.
2266
, doi: .
Nilsson
,
F.
,
Silva
,
N.
and
Schelin
,
J.
(
2024
), “
Single-use versus reusable packaging for perishable liquid foods-exploring evidence from research on climate impact and food safety
”,
Resources, Conservation and Recycling
, Vol. 
207
, 107655, doi: .
Otto
,
S.
,
Strenger
,
M.
,
Maier-Nöth
,
A.
and
Schmid
,
M.
(
2021
), “
Food packaging and sustainability–consumer perception vs. correlated scientific facts: a review
”,
Journal of Cleaner Production
, Vol. 
298
, 126733, doi: .
Parsons
,
R.
(
2022
), “
The role of plastic packaging in transforming food retailing
”,
British Food Journal
, Vol. 
124
No. 
4
, pp. 
1285
-
1300
, doi: .
Plastic Oceans, I
(
2023
), “
Plastic pollution facts
”,
Plastic Oceans
.
Plastic Soup Foundation, I
(
2023
), “
Single-use plastics
”,
Plastic Soup Foundation
.
Reyes-Jurado
,
F.
,
Soto-Reyes
,
N.
,
Dávila-Rodríguez
,
M.
,
Lorenzo-Leal
,
A.
,
Jiménez-Munguía
,
M.
,
Mani-López
,
E.
and
López-Malo
,
A.
(
2023
), “
Plant-based milk alternatives: types, processes, benefits, and characteristics
”,
Food Reviews International
, Vol. 
39
No. 
4
, pp. 
2320
-
2351
, doi: .
Roden
,
J.
(
2024
), “
Too hard to recycle: calls to ban some coloured plastic bottles
”.
Roy
,
D.
,
Berry
,
E.
and
Dempster
,
M.
(
2022
), “
‘If it is not made easy for me, I will just not bother’. A qualitative exploration of the barriers and facilitators to recycling plastics
”,
PLoS One
, Vol. 
17
No. 
5
, e0267284, doi: .
Rundle-Thiele
,
S.
,
David
,
P.
,
Willmott
,
T.
,
Pang
,
B.
,
Eagle
,
L.
and
Hay
,
R.
(
2019
), “
Social marketing theory development goals: an agenda to drive change
”,
Journal of Marketing Management
, Vol. 
35
Nos
1-2
, pp. 
160
-
181
, doi: .
Rundle-Thiele
,
S.
,
Dietrich
,
T.
and
Carins
,
J.
(
2021
), “
CBE: a framework to guide the application of marketing to behavior change
”,
Social Marketing Quarterly
, Vol. 
27
No. 
3
, pp. 
175
-
194
, doi: .
Saunders
,
M.
,
Lewis
,
P.
and
Thornhill
,
A.
(
2019
),
Research Methods for Business Students
, (9th ed.) ,
Pearson Education
,
Harlow
.
Schymanski
,
D.
,
Goldbeck
,
C.
,
Humpf
,
H.-U.
and
Fürst
,
P.
(
2018
), “
Analysis of microplastics in water by micro-raman spectroscopy: release of plastic particles from different packaging into mineral water
”,
Water Research
, Vol. 
129
, pp. 
154
-
162
, doi: .
Stefanini
,
R.
,
Borghesi
,
G.
,
Ronzano
,
A.
and
Vignali
,
G.
(
2021
), “
Plastic or glass: a new environmental assessment with a marine litter indicator for the comparison of pasteurized milk bottles
”,
International Journal of Life Cycle Assessment
, Vol. 
26
No. 
3
, pp. 
767
-
784
, doi: .
Thaler
,
R.H.
and
Sunstein
,
C.R.
(
2009
),
Nudge: Improving Decisions About Health, Wealth, and Happiness
,
Penguin
.
Truelove
,
H.B.
,
Largo-Wight
,
E.
,
Siuda
,
A.N.S.
,
Gowans
,
S.
,
Minichiello
,
H.
and
Hill
,
J.
(
2023
), “
Reducing single-use plastic on college campuses: theory of planned behavior-based brief interventions
”,
Current Research in Ecological and Social Psychology
, Vol. 
4
, 100098, doi: .
Van Hau
,
P.
(
2024
), “
Rethinking single-use plastics: behavioural insights and lessons from a developing nation
”,
Environmental Challenges
, Vol. 
17
, 101052, doi: .
Van Hau
,
P.
,
Robertson
,
K.
,
Thyne
,
M.
,
Hamlin
,
R.
and
Rundle-Thiele
,
S.
(
2025a
), “
Reducing single-use plastics (SUPs) consumption: a synthesis of I and S level approaches
”,
Sustainable Futures
, Vol. 
10
, 101087, doi: .
Van Hau
,
P.
,
McIver
,
T.
,
Robertson
,
K.
and
Thaichon
,
P.
(
2025b
), “
Effective customer segmentation using the recency, frequency, and monetary framework, combined with density-based clustering
”,
Journal of Strategic Marketing
, pp. 
1
-
23
, doi: .
Van Selm
,
B.
,
Frehner
,
A.
,
De Boer
,
I.J.
,
Van Hal
,
O.
,
Hijbeek
,
R.
,
Van Ittersum
,
M.K.
,
Talsma
,
E.F.
,
Lesschen
,
J.P.
,
Hendriks
,
C.M.
,
Herrero
,
M.
and
van Zanten
,
H.H.E.
(
2022
), “
Circularity in animal production requires a change in the EAT-lancet diet in Europe
”,
Nature Food
, Vol. 
3
No. 
1
, pp. 
66
-
73
, doi: .
WasteMINZ
(
2020
), “
The truth about plastic recycling in aotearoa New Zealand in 2020
”.
Winkler
,
A.
,
Santo
,
N.
,
Ortenzi
,
M.A.
,
Bolzoni
,
E.
,
Bacchetta
,
R.
and
Tremolada
,
P.
(
2019
), “
Does mechanical stress cause microplastic release from plastic water bottles?
”,
Water Research
, Vol. 
166
, 115082, doi: .
Zhang
,
Q.
,
Liu
,
L.
,
Jiang
,
Y.
,
Zhang
,
Y.
,
Fan
,
Y.
,
Rao
,
W.
and
Qian
,
X.
(
2023
), “
Microplastics in infant milk powder
”,
Environmental Pollution
, Vol. 
323
, 121225, doi: .
Published by Emerald Publishing Limited. This article is published under the Creative Commons Attribution (CC BY 4.0) license. Anyone may reproduce, distribute, translate and create derivative works of this article (for both commercial and non-commercial purposes), subject to full attribution to the original publication and authors. The full terms of this license may be seen at Link to the terms of the CC BY 4.0 licence.

Supplementary data

or Create an Account

Close Modal
Close Modal