The Value of Transdisciplinary Perspectives During Transition to a Bio-based Economy: The Prospect for Converting Mixed Food Waste into Bio-based Chemicals

Within the current political and industrial transition to a bio-based economy, food waste can be an alternative resource for biobased chemicals. This chapter describes a case study that evaluates the prospect for Swedish production of biobased chemicals such as succinic acid from food waste. The evaluation is addressed from multiple systems perspectives. From a technical and resource system perspective, the results of the case study show that production seems possible. However, from a social system perspective succinic acid production currently lacks institutional support and actor commitment and alignment for realizing development in Sweden. From an environmental and life cycle perspective, the scoping of the analysis is decisive for the results. The study shows that multiple perspectives complement each other when seeking a nuanced evaluation of technical innovation and give insights for the intended value chain. determine if there is suf ﬁ cient mixed food waste in Sweden for that production capacity. The results show that there is suf ﬁ cient mixed food waste in Sweden as a whole, but not in individual facilities. Further, scenario analysis (including material ﬂ ow analysis and policy analysis) was used to assess if there is suf ﬁ cient mixed food waste in Sweden for the production capacity, also given political goals to minimize avoid-able food waste. The results show that there are suf ﬁ cient ﬂ ows in Sweden, although distributed among sites in a large geographical area. Further details can be found in related work of Rex et al. [7].


Introduction
In line with current political and industrial ambitions for a transition into a bio-based economy, food waste can be an alternative to agro-and forest-based resources. The amount of food waste generated every year is about 1.3 billion tons globally [1]. This wasted food has caused problems related to climate change and resource depletion throughout their value chains, as well as increasing economic challenges related to waste disposal.
Some of these problems could be eased by converting food waste into valuable products like bio-based chemicals. Succinic acid (SA) is one such chemical with high market potential [2]. Today, it is produced from fossil sources but also partly from cultivated biomass on a commercial basis [3]. Several initiatives are now underway to examine the use offood waste as feedstock for SA production. Most of these initiatives are limited to homogenous industrial waste streams, but a research project in Sweden is looking at a more novel and complex feedstock-mixed food waste (MFW) [4].
The purpose of this project is to evaluate the prospect for realizing Swedish production of bio-based chemicals from MFW. In this chapter, we present the evaluation results of one possible production route, where microbial production of SA from MFW in Sweden is used as a case study.
The evaluation of SA from MFW is addressed from multiple perspectives: technical and social system structures are explored, in addition to resource and environmental implications. Several perspectives and methods are thus involved in the evaluations, such as the technical (laboratory cultivation and mechanical testing), the social (actor analysis, policy analysis, market analysis, and societal acceptance), the resource based (waste flow analysis and scenario analysis), and the environmental (life cycle assessment of current and future valorization techniques for MFW). The project thus uses a transdisciplinary approach and offers an arena where both research partners and industrial partners meet and discuss possible options for MFW-based SA production in Sweden.

Multiple Perspectives and Evaluation Methods for Converting Mixed Food Waste into Bio-based Chemicals
The case study chosen here involves microbal growth on mixed food waste derived from municipal solid waste to produce bio-based SA in Sweden. The mixed food waste was sourced from Ragn Sells AB's full-scale waste management facility in the area of Stockholm, Sweden. In Sweden, the current value pathway for MFW involves anaerobic digestion to produce biogas [5]. The future production could involve the cultivation of Escherichia coli bacteria to produce succinic acid as a raw material for further polymerisation. The case study was chosen together with academic and industrial partners in a multidisciplinary research project on how mixed food waste can be used as a resource for the production of bio-based chemicals and higher value products than current biogas (FORMAS 211-2012-70). Research questions derived from different partners included different disciplines, such as molecular biology (natural science), biotechnology (bio-based engineering), as well as social systems perspectives (social science) and environmental systems science (resource and life cycle perspective). Multiple perspectives, scales and methods were thus involved in the different evaluations presented in Table 1, which lead to different results presented in the following sections.

Technical Evaluation Performed on Lab Scale
Several research questions and methods are involved in the technical evaluation e.g. laboratory cultivation and mechanical testing. By the use of elementary analysis, the composition of substances/molecules in mixed food waste was identified. The results show that mixed food waste contains required N and C for E.coli growth, although additional N would increase C use. Enzymatic hydrolysis and carbohydrate analysis was then used to show how the carbon sources included could be made more accessible for E.coli uptake [6]. Through laboratory cultivating tests it was assessed if E.coli could grow on mixed food waste. The results show that the liquid fraction of the waste supports growth and the solids can be used as carbon source. To determin if the water content of MFW was optimal for E.coli growth, mechanical property tests were made. The results show that the water content was too high for industrial production, described in Rex et al. [7].

Social Evaluation Based on Innovation Systems
Several research questions and methods were also involved in the social system evaluation, e.g. policy analysis, analysis of societal acceptance, actor and market analyses. A policy analysis was performed to assess how existing rules and regulations influence the possibility to realize SA production from mixed food waste in Sweden. The main source of data for the analysis were documents on policy directives and instruments complemented with workshops and interviews with focus groups. A key result is that there are hardly any policy instruments supporting bio-based chemical development on national and EU level. So far there exists only declarations of intent in various policy documents and reports and limited R&D subsidies. Another key result is that subsidies and investments in the development of biofuels, in particular biogas, for the transport sector influence the access of feedstock for the production of bio-based chemicals and might contribute to increased competition in the future. Societal acceptance is essential for the legitimacy of an innovation and to assess how norms and values in society influence the prospects of producing SA from mixed food waste. The main source of data for the analysis were interviews and workshops complemented with analysis of discussions in related areas, such as GMO and food versus fuel (e.g. through newspaper articles, NGO webpages, and research reports). The results show that the perceptions of circularity of biomass and bio-based chemicals and related products are positive. However, public resistance towards genetically modified organisms has previously hampered the realization of a bio process production facility and may do so in the case of SA as well.
A screening of market data and scenarios was carried out to judge the future demand of increased SA production. The main source of data for the analysis were documents and literature on future market. The results indicate that there is a demand for bio-based SA and that it is expected to grow in the future considering bio-based SA can substitute a range of fossil chemical components, not only fossil SA. Also, there is an interest of producing and buying bio-based chemicals and related products in a more resource efficient manner, e.g. using waste instead of the currently used food crops.
Finally, a mapping of current and future actors was made to determine if the right type of actors can be mobilized to realize a SA value chain to enable the production facility. The results show that although technical competences exist and market demand is expected in the future, actors are not yet fully committed or aligned to develop bio-based chemicals production such as SA from food waste. Further details can be found in related work of Ulmanen et al. [8].

Resource Evaluation Based on Waste Flows
Several research questions and methods were involved in the resource evaluation e.g. material flow analysis and scenario analysis. The question of which capacity is needed for production of bio-based SA was approached using benchmark of existing and planned production sites for bio-based SA production. The results show that a capacity of at least 10,000 tons bio-based SA/year is likely to be needed for a commercial plant. Material flow analyses were used to determine if there is sufficient mixed food waste in Sweden for that production capacity. The results show that there is sufficient mixed food waste in Sweden as a whole, but not in individual facilities. Further, scenario analysis (including material flow analysis and policy analysis) was used to assess if there is sufficient mixed food waste in Sweden for the production capacity, also given political goals to minimize avoidable food waste. The results show that there are sufficient flows in Sweden, although distributed among sites in a large geographical area. Further details can be found in related work of Rex et al. [7].

Environmental Evaluation Based on the Life Cycle
In the environmental evaluation, a life cycle assessment of current and future systems was performed. Life cycle assessment with focus on valorisation options was used to analyse if the current biogas production or the future production of SA had the lowest environmental impacts as valorisation option for mixed food waste. The process description of biogas is based on an existing biogas facility in Heljestorp [9]. The process description used of food waste to succinic acid is based on lab-scale data with mixed food waste [10]. The results show that current biogas production has a better environmental performance on all main impacts categories used (global warming potential, energy use, acidification potential, eutrophication potential) than future production of SA with mixed food waste. In parallell, a life cycle assessment with focus on feedstocks was performed to adress the question: Do mixed food waste have a better environmental performance than current feedstocks for SA production? The process description of Corn to succinic acid has been chosen based on Reverdia Direct Crystallization process described in Cok et al. [11] and Smidt et al. [12]. The results show that a future use of mixed food waste likely would have a better environmental performance than current corn-based feedstocks. Further details on the comparison and evaluation can be found in related work of Carlson [13] and Brunklaus et al. [14].

Multiple Evaluations Show Complementing Results
As seen from above, multiple perspectives and methods are involved in the different evaluations and show complementing results. The results of the case study show that, even though from a technical and resource system perspective, production seems possible, from a social system perspective SA production currently lacks institutional support and actor commitment and alignment for realizing development in Sweden. From an environmental and life cycle perspective, the scoping of the analysis is decisive for the results: SA production from mixed food waste is environmentally beneficial if compared with the SA production from corn, but from a pure waste handling perspective, it is environmentally better to produce biogas than SA from mixed food waste.

Potentials and Limitations of Combined Systems Approaches
Different systems approaches provide guidance about current and future industrial systems. Each of the method approaches are based on different questions and provide different answers. To take this further, one has to understand some general approaches in systems science: What are the differences in goal and scope? What are the potentials and limitations of combined systems approaches?

Differences in Goal and Scope
Systems approaches are based on the goals and the scope of the study. To say something about how valid the different results of the multiple perspectives are in relation to each other, it is important to understand the object and the scope of analysis of each assessment, presented in Table 2.
In the technical evaluation, the object of analysis is the biotechnological possibilities and the scope of the study lies on the molecular scale and the laboratory scale. Results have to be seen per scale and technical indications can be made limited to the scale. The social evaluation was made as part of of a technological innovation systems analysis on national and EU scale. Here the scope and boundaries of the study is based on so called structural components, that includes technology, actors, networks and institutions. Institutions refers to formal policy rules and regulations as well as informal norms and values related to societal acceptance. In the resource evaluation, material flows are in focus and the scope and boundaries the study is based on the production scale and geographical scale. In the environmental evaluation, the object of analysis is physical flows of material, resources, waste and energy, and the scope and boundaries of the study is based on processes that are part of the life cycle of handling food waste and producing SA, respectively. Results for resource and environmental evaluations have to be seen per scale and indication have to be seen as well in temporal scale of current and future value chains.
Systems approaches as used in the example above require significant time and efforts, as well as expertise in different scientific areas. These are essential for complex problem solving, and are thus system dependent as described in Flood and Calsson [15]. The potential in relation to systems perspectives lies in knowledge creation. Knowledge is built on like building blocks, which together forms the basis for decision-making and the next step in the innovation process.

Potentials in Relation to Life Cycle Management
Taken together, the studies differ in both the objects of analysis and the scope and boundaries in which the results are valid. Moreover, methods used derive from different research traditions and method approaches such as the analytical, the system and the social approaches described in Arbor and Bjerke [16] and Wolf [17]. Due to different research traditions and method approaches and their fundamental discrepancies, and the related amount of work and efforts made, it might be questionable to relate answers from these perspectives in the same assessment, as is the case in the example above. Yet we argue that for Life Cycle Management, assessing multiple perspectives and transdiciplinary approaches is a valuable way of working. Life Cycle Management is about decreasing the negative impact of physical flows in society, by approaching the acts and practices of actors in the system. In this respect, there is a need to understand the premises for success in everything from technological possibilities in lab scale to the amount of materials available in a region, and the norms, values and intentions of actors needed to develop the system. Thus, combined systems studies should, with careful respect to the differences in goal and scope, be seen as complementary studies to guide technology innovation. Insights form these multiple perspectives can be of value for any actor aiming to manage these systems for the advances of less environmental impact from a life cycle perspective. Further research on evaluating various actors might give some insights on of how useful the various systems studies were in the collaboration, and toward decision making. To this end, the above perspectives are seen as complementary, yet not exhaustive. An important perspective not included in the above is an assessment of the economic feasibility of SA from MFW. Also combining SA with other products in a bio-refinery has not been evalutated, to give some examples.

Conclusion
Combined-systems approaches and multiple methods contribute with a useful holistic perspective to evaluate and guide technology innovation from a life cycle perspective. Results from a case study on bio-based SA does not provide a unanimous answer on whether the prospects for transforming MFW into bio-based chemicals are favorable or not, but gives a nuanced evaluation that offers a more firm foundation for decision and further development than one perspective or method in isolation. The transdisciplinary approach can inform an arena of research and industrial partners with different perspectives to facilitate discussion and more well-informed decisions. Despite time and efforts, the case thus illustrates the benefits of applying a transdisciplinary approach with multiple perspectives when assessing and evaluating potential routes to a more bio-based economy, and when seeking to manage the progress of sustainable value chains. Open Access This chapter is licensed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license and indicate if changes were made. The images or other third party material in this chapter are included in the chapter's Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the chapter's Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder.