Abstract The management of the plastic fraction is one of the most debated issues in the discussion on integrated municipal solid waste systems. Both material and energy recovery can be performed on such a waste stream, and different separate collection schemes can be implemented. The aim of the paper is to contribute to the debate, based on the analysis of different plastic waste recovery routes. Five scenarios were defined and modelled with a life cycle assessment approach using the EASEWASTE model. In the baseline scenario (P0) the plastic is treated as residual waste and routed partly to incineration with energy recovery and partly to mechanical biological treatment. A range of potential improvements in plastic management is introduced in the other four scenarios (P1–P4). P1 includes a source separation of clean plastic fractions for material recycling, whereas P2 a source separation of mixed plastic fraction for mechanical upgrading and separation into specific polymer types, with the residual plastic fraction being down-cycled and used for “wood items”. In P3 a mixed plastic fraction is source separated together with metals in a “dry bin”. In P4 plastic is mechanically separated from residual waste prior to incineration. A sensitivity analysis on the marginal energy was carried out. Scenarios were modelled as a first step assuming that marginal electricity and heat were based on coal and on a mix of fuels and then, in the sensitivity analysis, the marginal energy was based on natural gas. The study confirmed the difficulty to clearly identify an optimal strategy for plastic waste management. In fact none of the examined scenarios emerged univocally as the best option for all impact categories. When moving from the P0 treatment strategy to the other scenarios, substantial improvements can be obtained for “Global Warming”. For the other impact categories, results are affected by the assumption about the substituted marginal energy. Nevertheless, irrespective of the assumptions on marginal energy, scenario P4, which implies the highest quantities of specific polymer types sent to recycling, resulted the best option in most impact categories.
[1]
J. Baeyens,et al.
Recycling and recovery routes of plastic solid waste (PSW): a review.
,
2009,
Waste management.
[2]
Mario Grosso,et al.
Influence of assumptions about selection and recycling efficiencies on the LCA of integrated waste management systems
,
2009
.
[3]
David Lazarevic,et al.
Plastic waste management in the context of a European recycling society: Comparing results and uncertainties in a life cycle perspective
,
2010
.
[4]
Jacob Møller,et al.
SEWAS (Sustainable European Waste Systems) Life cycle assessment of prospective integrated waste management schemes
,
2012
.
[5]
David Pennington,et al.
Recent developments in Life Cycle Assessment.
,
2009,
Journal of environmental management.
[6]
Brian Vad Mathiesen,et al.
Energy system analyses of the marginal energy technology in life cycle assessments
,
2007
.
[7]
Maria Laura Mastellone,et al.
Life Cycle assessment of a plastic packaging recycling system
,
2003
.
[8]
Lucia Rigamonti,et al.
Material and energy recovery in integrated waste management systems. An evaluation based on life cycle assessment.
,
2011,
Waste management.
[9]
Janus T Kirkeby,et al.
Environmental assessment of solid waste systems and technologies: EASEWASTE
,
2006,
Waste management & research : the journal of the International Solid Wastes and Public Cleansing Association, ISWA.
[10]
Maria Laura Mastellone,et al.
A life cycle assessment of mechanical and feedstock recycling options for management of plastic packaging wastes
,
2005
.