Abstract
The Brazilian National Solid Waste Policy Law promotes sustainable integrated solid waste management nationally, and is committed to improve “informal” recyclable waste pickers’ socio-economic conditions. This has led municipalities to develop waste management strategies to incorporate “informal” waste pickers into the “formal” system. In order to measure the social improvement achieved by this action, it is necessary to define a set of indicators capable of quantifying the social performance of waste management systems that adapt specifically to developing countries.
In this study, a set of social impact categories, indicators and metrics capable of assessing the socio-economic and labour conditions of the different stakeholders involved in the life cycle of a municipal solid waste management (MSWM) system is proposed. Then they are applied to a case study in the city of João Pessoa, Paraíba (Brazil). João Pessoa is one of the pioneering Brazilian cities to incorporate a door-to-door selective waste collection system managed by the previous “informal” waste pickers, reorganised into associations or cooperatives of collectors of recyclable materials. Although this waste collection system has steadily expanded around the city until the present-day, it has never been analysed from a social perspective.
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9.1 Introduction
Waste management covers a vast field of human activities which, in developing countries, share some similarities to their social singularities, such as limited participation in selective collection programmes, or waste pickers’ poor socio-economic and labour conditions [1].
By taking Brazil as a case study, the National Brazilian Solid Waste Policy Law [2] encourages sustainable integrated solid waste management nationally by improving the working conditions of informal waste pickers by integrating them into formal waste picker cooperatives [3]. Among other actions, this aims to improve the social performance of the Municipal Solid Waste Management (MSWM) systems.
To assess and improve MSWM systems in developing countries, it is necessary to evaluate them from a life cycle perspective, including the assessment of social aspects [4]. However, no consensus has been reached for the social impact assessment method, neither in the impact categories to be used, nor in the stakeholders to be considered [5]. Therefore, in order to analyse the social performance of MSWM systems, it is necessary to define an adequate set of social categories, indicators and metrics and the groups of stakeholders to be taken into account.
With this context in mind, the present research aims to propose and apply a set of social indicators capable of assessing the socio-economic and labour conditions of the different stakeholders involved in the life cycle of an MSWM system in developing countries in general, and in Brazil in particular. To do so, a set of social impact categories, indicators and metrics is proposed after taking into account the needs and characteristics of developing countries and the conclusions drawn from a literature review of social impacts caused by waste management activities worldwide. These proposed social indicators were applied to a case study in João Pessoa (Brazil).
9.2 Methodology
The methodology used for proposing and applying to the case study a set of social indicators and metrics to assess the social performance of MSWM systems in developing countries in general, and in Brazil in particular, consists in the stages showed in Fig. 9.1 and described below.
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1.
A literature review that focuses on analysing the social impact categories/indicators of system in order to identify those more commonly applied. It has been mostly observed that the reviewed studies are based on the methodological framework proposed by UNEP-SETAC [6, 7].
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2.
A literature review that focuses on analysing MSWM systems in order to identify the stages, the involved stakeholders, socio-economic and labour conditions, needs, etc. of MSWM systems implemented in developing countries in general, and in Brazil in particular.
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3.
Proposing a set of social impact categories, with their corresponding indicators, capable of assessing the socio-economic and labour conditions of the stakeholders involved in the life cycle of an MSWM system by taking into account the information from Stages I and II. In order to quantify each indicator, metrics and data source were proposed for each stakeholder that affects it. A set of 12 social impact categories and 22 indicators, with their corresponding metrics, are suggested (for details see Table 9.1).
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4.
Gathering site-specific information for each metric to apply the proposed social impact categories and indicators to the case study. To do this, questionnaires have to be specifically devised for each group of involved stakeholders.
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5.
A weighting process need to be applied to merge the metrics for each indicator. A multi-criteria decision analysis is recommended to take into account different preferences for the various social impact categories/indicators [8].
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6.
The calculated social indicators can be graphically represented to facilitate the identification of the social impact categories/indicators that perform better or worse, or to compare different case studies. To do this, spider graphs may be represented by considering that the bigger the drawn area, the better the system’s performance. That is to say, the best social performance of a category would receive the maximum score (100%) and would be plotted on the more external line of the spider graph.
9.3 Case Study
The proposed methodology was applied to a case study in the Brazilian city of João Pessoa, whose population (791,000 inhabitants) produces more than 247,000 tons of municipal solid waste per year [9]. The MSWM system in João Pessoa has progressively incorporated a selective collection programme since 2003 [10]. Consequently, different informal waste pickers who previously collected recyclable materials in open dumps have been reorganised in associations that are in charge of door-to-door recyclable material collection and of the manual segregation of recyclable materials in a new manual Material Recovery Facility (MRF) located next to the sanitary landfill. See Fig. 9.2.
To apply the methodology, the site-specific data needed to quantify each metric were collected from the involved stakeholders: workers (waste pickers), users (waste producers) and municipal authorities. To this end, questionnaires were designed for each stakeholder group and were tested by a small sample of surveyed individuals to see if the language was comprehensible, if the response options were suitable and if the necessary information for quantifying the indicators was acquired. Moreover, additional information was obtained from the observations made when visiting the facilities.
The obtained results are presented in Fig. 9.3.
9.4 Conclusions
The proposed methodology allows the social performance of waste management systems in developing countries to be assessed. This methodology is based on a proposal of social impact categories, and indicators and metrics that facilitate their quantification.
The proposed social impact categories and indicators were applied and validated to the case study of the city of João Pessoa (Brazil). The obtained results demonstrate how the social performance of the MSW management system in João Pessoa still has room for improvement from a social point of view. The better performing social indicators are “Working hours and/or weekly rest” and “Safe and healthy living conditions”, followed by “Customer/citizen satisfaction”. The worst performing social indicators are “Labour regulation” and “Fair salary”, followed by “Social characteristics of population” and “Legal employment with social benefits/security”.
Although it has been demonstrated that the proposed social impact categories and indicators are practicable and successful for identifying key aspects and for extending knowledge on the social performance of the MSW management system in the case study, some suggestions for future development are identified. Analysing not only the social characteristics of workers and their families, but those of the users involved in the waste management system, and of the local communities living next to the facilities involved in the system, seems interesting to obtain in-depth knowledge about the effect of the system on its backyard. In line with this, adding an impact category related to some physical impacts, generally considered environmental aspects (e.g. noise, odour, visual impact, etc.), could provide profound knowledge about the analysed systems as these aspects could be important for waste management sites to be accepted by neighbourhoods. Finally, more information about workers’ living conditions, such as house size or the security at home, would provide a more detailed picture of the “safe and healthy living conditions” indicator. In addition, previous training about aspects related to occupational diseases, occupational safety and health measures, etc., is highly recommendable to ensure that waste workers correctly understand the questionnaires.
The proposed social impact categories and indicators allow the identification of both the social issues and social benefits associated with the inclusion of the informal waste management sector in municipal management strategies in developing countries, which can help in the decision making that forms part of steering municipal programmes for social performance improvement.
References
Aparcana S, Salhofer S. Development of a social impact assessment methodology for recycling systems in low-income countries. Int J Life Cycle Assess. 2013;18:1–10.
Lei 12305 de 2 de agosto de 2010. Institui a Política Nacional de Resíduos Sólido, 2010.
Magni AAC, Günther WMR. Cooperatives of waste pickers as an alternative to social exclusion and its relationship with the homeless population. Saúde e Sociedade. 2014;23:99–109.
Vinyes E, Oliver-Solà J, Ugaya C, Rieradevall J, Gasol CM. Application of LCSA to used cooking oil waste management. Int J Life Cycle Assess. 2013;18:445–55.
Yıldız-Geyhan E, Altun-Çiftçioğlu GA, Kadırgan MAN. Social life cycle assessment of different packaging waste collection system. Resour Conserv Recycl. 2017;124:1–12.
UNEP-SETAC. Guidelines for social life cycle assessment of products. Paris: United Nations Environment Programme; 2009.
UNEP-SETAC. The methodological sheets for subcategories in social life cycle assessment (S-LCA). United nations environment programme; 2013.
Azapagic A, Perdan S. An integrated sustainability decision-support framework part II: problem analysis. Int J Sust Dev World. 2005;12:112–31.
IBGE. Estimativa da População: Paraíba-João Pessoa. Brazil: Instituto Brazileiro de Geografia e Estatística; 2015.
Coutinho-Nóbrega C. Viabilidade Econômica, com Valorização Ambiental e Social, de Sistemas de Coleta Seletiva de Resíduos Sólidos Domiciliares – Estudo de Caso: João Pessoa/PB. Brazil: Universidade Federal de Campina Grande; 2003.
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Ibañez-Forés, V., Bovea, M.D., Coutinho-Nóbrega, C. (2020). Proposal of Social Indicators to Assess the Social Performance of Waste Management Systems in Developing Countries: A Brazilian Case Study. In: Traverso, M., Petti, L., Zamagni, A. (eds) Perspectives on Social LCA. SpringerBriefs in Environmental Science. Springer, Cham. https://doi.org/10.1007/978-3-030-01508-4_9
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