It is of utmost importance to collect organic waste from households as a separate waste stream. If collected separately, it could be used optimally to produce compost and biogas, it would not pollute fractions of materials that can be recovered from residual waste streams and it would not deteriorate the quality of some materials in residual waste (e.g. paper). In rural areas with separate organic waste collection systems, large quantities of organic waste are recovered. However, in the larger cities, only a small fraction of organic waste is recovered. In general, citizens dot not have space to store organic waste without nuisances of smell and/or flies. As this has been the cause of low organic waste collection rates, collection schemes have been cut, which created a further negative impact. Hence, additional efforts are required. There are some options to improve the organic waste recovery within the current system. Collection schemes might be improved, waste containers might be adapted to better suit the needs, and additional underground organic waste containers might be installed in residential neighbourhoods. There are persistent stories that separate organic waste collection makes no sense as the collectors just mix all municipal solid waste after collection, and incinerate it. Such stories might be fuelled by the practice that batches of contaminated organic waste are indeed incinerated. Trust in the system is important. Food waste is often regarded as unrein. Users might hate to store food waste in their kitchen that could attract insects, or the household pets. Hence, there is a challenge for socio-psychological research. This might also be supported by technology, e.g. organic waste storage devices and measures to improve waste separation in apartment buildings, such as separate chutes for waste fractions. Several cities have experimented with systems that collect organic wastes by the sewage system. By using a grinder, kitchen waste can be flushed into the sewage system, which in general produces biogas by the fermentation of sewage sludge. This is only a good option if the sewage is separated from the city drainage system, otherwise it might create water pollution. Another option might be to use grinders, that store the organic waste in a tank. This tank could be emptied regularly by a collection truck. Clearly, the preferred option depends on local conditions and culture. Besides, the density of the area, the type of sewage system and its biogas production, and the facilities that are already in place for organic waste collection are important parameters. In the paper, we will discuss the costs and benefits of future organic waste options and by discussing The Hague as an example.
DOCUMENT
From the article: "This article evaluates the application of blockchain technology to improve organic or fair-trade food traceability from “Farm to Fork” in light of European regulations. This study aims to shed light on the challenges in the organic food chain to overcome, the drivers for blockchain technology, and the challenges in current projects."
DOCUMENT
One behavioural intervention that can help increase the opportunity to separate organic waste is offering a organic waste bin and bags. But which type of bin is best to offer to residents, do you give a choice or not, and how can you best manage the distribution? We tried to answer these questions through a study on the use of organic waste bins in the Netherlands.
DOCUMENT
If you, as a municipality or waste collector, you want to learn more abouthow residents view to the separation of organic waste and at the same timeencourage them to separate their organic waste (better), then the infosurveymay be an interesting solution. This is a survey and behavioural interventionin one. The infosurvey can be used in a neighborhood where organic wastecan be separated.
DOCUMENT
This chapter offers an account of a workshop in arts-based learning called “Metamorphoses of Organic Forms”. This detailed description of a particular practice may inform a discussion of ways in which artful approaches, in general, may come to matter in STEAM education, with implications for both educational research and practice. Added to that, the chapter argues that such art-based practices can also be relevant more widely in the context of sustainability education, such as on the theme of climate change. Precisely because the content of the art workshop at hand is not prima facie linked to it, there is an unexpected potential to take up such a tangential theme in an unusual way. Typically, participants feel invigorated to enter new territory – both spatial and mental. On a meta-level, the session can also be seen as a practice in facing complexity, uncertainty, not knowing. The chapter suggests that such artful educational practices have intrinsic merit if we are to equip new generations with skills to live in and endure “post-normal times”. In the workshop “Metamorphoses of Organic Forms”, participants are invited to imagine how forms in nature might either evolve or disintegrate over time. The workshop lends itself to follow-up lessons in biology and natural history. The outcome is not given. Participants go through a shared process step by step, following a sequence that is outlined for them as they go along. They are encouraged to imagine how natural phenomena might grow or decay in time and they do this in a series of short sessions where they sculpt works in clay. Such a practice in art-based environmental education is arguably a form of “poor pedagogy”. This educational activity is primarily and fundamentally an open-ended process. Rather than requiring an extensive methodology, its practice requires participants to surrender themselves to a process that will be unique each time it is performed. Such a practice is an expression of a view on education that is not centred on the transmission of knowledge but rather looks at attention as education and the education of attention.
DOCUMENT
This report shows the findings after two years of applied research in the BASSTA Plus project. It focuses on conducting neighbourhood analyses, testing behavioural interventions and monitoring and evaluating them. All with the objective to let residents separate organic waste more and/or better.
MULTIFILE
The paper forms a rejoinder to the paper by David Weaver ('Organic, incremental and induced paths to sustainable mass tourism convergence'). It fully agrees with David Weaver that a sustainable development of tourism should focus on sustainable mass tourism development and not, as is currently the case, so much on niche products labelled 'sustainable'. However, it critiques Weaver's operationalization of sustainability, his assumption that sustainable mass tourism (SMT) will be the 'emergent norm' due to external factors, and his destination development theory showing different paths that, however, all end in SMT. Finally it is shown that the path development idea might be at odds with systems thinking.
LINK
This research contributes to understanding and shaping systems for OFMSW separation at urban Small and Medium Enterprises (SMEs, such as offices, shops and service providers). Separating SMEs’ organic fraction of municipal solid waste (OFMSW) is both an opportunity and a serious challenge for the transition towards circular cities. It is an opportunity because OFMSW represents approximately 40% of the total waste mass generated by these companies. It is challenging because post-collection separation is not feasible for OFMSW. Therefore, SMEs disposing of waste should separate their solid waste so that processing the organic fraction for reuse and recycling is practical and attainable. However, these companies do not experience direct advantages from the extra efforts in separating waste, and much of the OFMSW ends up in landfills, often resulting in unnecessary GHG emissions. Therefore, governments and waste processors are looking for ways to improve the OFMSW separation degree by urban companies disposing of waste through policies for behaviour change.There are multiple types of personnel at companies disposing of waste. These co-workers act according to their values, beliefs and norms. They adapt their behaviour continuously, influenced by the physical environment, events over time and self-evaluation of their actions. Therefore, waste separation at companies can be regarded as a Socio-Technical Complex Adaptive System (STCAS). Agent-based modelling and simulation are powerful methods to help understand STCAS. Consequently, we have created an agent-based model representing the evolution of behaviour regarding waste separation at companies in the urban environment. The model aims to show public and private stakeholders involved in solid waste collection, transport and processing to what extent behaviour change policies can shape the system towards desired waste separation degrees.We have co-created the model with participants utilising literature and empirical data from a case study on the transition of the waste collection system of a business park located at a former harbour area in Amsterdam, The Netherlands. First, a conceptual model of the system and the environment was set up through participatory workshops, surveys and interviews with stakeholders, domain experts and relevant actors. Together with our case participants, five policies that affect waste separation behaviour were included in the model. To model the behaviour of each company worker’s values, beliefs and norms during the separation and disposal of OFMSW, we have used the Value-Belief-Norm (VBN) Theory by Stern et al. (1999). We have collected data on waste collection behaviour and separation rates through interviews, workshops and a literature study to operationalise and validate the model.Simulation results show how combinations of behaviour profiles affect waste separation rates. Furthermore, findings show that single waste separation policies are often limitedly capable of changing the behaviour in the system. Rather, a combination of information and communication policies is needed to improve the separation of OFMSW, i.e., dissemination of a newsletter, providing personal feedback to the co-workers disposing of waste, and sharing information on the (improvement of) recycling rates.This study contributes to a better understanding of how policies can support co-workers’ pro-environmental behaviour for organic waste separation rates at SMEs. Thus, it shows policymakers how to stimulate the circular transition by actively engaging co-workers’ waste separation behaviour at SMEs. Future work will extend the model’s purpose by including households and policies supporting separating multiple waste types aimed at various R-strategies proposed by Potting et al. (2016).
MULTIFILE
The increase in consumption of resources has led to more waste being generated, which then needs to be managed at the end of their life-cycle as waste. Current practices of waste management are not efficient as they lead to a release of emissions and a loss of value that is present in the resource, which is discarded as waste. New legislation for efficient waste management practices has been established, however, adopting them is hampered by factors, one of which is the high cost of these solutions. However, incentive-based approaches can be used to address this problem. This research explores the role of institutional incentives in the form of property rights bundles for such cases. Property rights are a set of formal and informal rules that define how resource allocation is done, while property rights bundles are the set of one or more property rights tied together. As per academic literature, a clear allocation of property rights leads to an economically efficient distribution of costs, benefits, risks and responsibilities associated with a resource. Based on these aspects, this research explores the influence of property rights bundles in the case of collective ownership of waste processing infrastructure by companies. Through collective ownership of the infrastructure, the investment cost would be distributed among those using the resource, thereby reducing the share of investment per company and addressing the challenge of high investment costs. Furthermore, in this situation of collective ownership, property rights need to be defined clearly so that there are no conflicts among the participants at later stages. The research is based on a case study of a few companies in Amsterdam, who are attempting to set up an initiative to improve the waste management practice in the region. For this purpose, they plan to invest collectively in a waste-processing infrastructure. This research thus explores the role of property rights in this regard. The literature on property rights forms the theoretical foundation of the research, along with the Theory of Planned Behaviour, which is the behavioural theory chosen to analyse the decision-making of the companies. The case study was analysed using the Institutional Analysis and Development framework. An agent-based model was built based on the insights obtained from these concepts to capture the interaction between the property rights and the characteristics of the companies, such as the amount of waste generated by them, the amount of budget they hold, etc. The influence of property rights bundles was analysed using the attributes of property rights: robustness, strength, duration and excludability. The results obtained were analysed using the defined Key Performance Indicators: Joining Ratio, Number of Participants and Number of times the initiative is started. It was found that for the case of the Amsterdam Zuidoost initiative, providing property rights bundles of claimants and proprietors as incentives leads to an increase in the number of participants that join the initiative. However, due to lack of statistical significance between the distributions, we cannot determine which of the two has a higher influence. Furthermore, the influence of the other property rights bundle could not be verified due to lack of statistical significance in the distribution.
MULTIFILE
This paper describes a study into consumers' reasons for buying socially responsible (SR) products, such as Fair Trade products and organic meat. As opposed to other studies, we use a qualitative approach based on 25 in-depth interviews and include several different products in the research. This leads to several new results, such as: (1) buying SR products is perceived as an imperfect moral duty; (2) low quality of SR products is a dissatisfier, but high quality not a satisfier; (3) the attitude towards SR products is related to the reputation of charitable funds; (4) the demand for SR products is negatively related to the frequency of purchasing SR products; (5) reflection on SR products raises the demand for SR products; (6) consumers that have witnessed the social problems that SR products aim to alleviate purchase more SR products. Finally, we find that the demand for different SR products is correlated: if a consumer buys one SR product, it is more likely that (s)he purchases other SR products as well.
DOCUMENT
