LCA of spent fluorescent lamps in Thailand at various rates of recycling

Abstract This paper presents environmental impact of a fluorescent lamp (a long straight tube 36 watts, 200 g and 13,600 h for mean time before failure) when considering different disposal methods (recycle and non-recycle) of its spent fluorescent lamp (SFL). The study was applied for the case in Thailand using life cycle assessment (LCA) as a tool. All materials, energy use, and pollutant emissions to the environment from each related process were identified and analyzed. Impact assessment was conducted for 10 environmental impact potentials: carcinogens, respiratory organics, respiratory inorganics, climate change, radiation, ozone layer, ecotoxicity, acidification/eutrophication, land use and minerals. The analysis followed Eco-Indicator 99 method, individualist version 2.1. The main focus of the study was to compare the impact of SFL recycling with non-recycling before landfilling. The impact intermittent activities, production of raw material and energy used in all the concerned processes were taken into account. However, transportation activities were excluded. The results showed that for all recycling rates, cement production is the main contributor to the environmental impacts, while sodium sulfide production is second and electrical production, the third. Mercury vapor emission showed a small contribution in carcinogens and ecotoxicity. The impacts are reduced when recycling rate is increased. The reduction of cement consumption in disposal processes or the process improvement of cement production may also help to reduce environmental impacts.

[1]  Henrik Wenzel,et al.  Integration of environmental aspects in product development: a stepwise procedure based on quantitative life cycle assessment , 2002 .

[2]  G. J. McRae,et al.  ENVIRONMENTALLY CONSCIOUS CHEMICAL PROCESS DESIGN , 1998 .

[3]  T. Graedel Industrial Ecology , 1995 .

[4]  J. G. Petrie,et al.  Life cycle assessment applied to process design: Environmental and economic analysis and optimization of a nitric acid plant , 1996 .

[5]  Adisa Azapagic,et al.  Life cycle Assessment and its Application to Process Selection, Design and Optimisation , 1999 .

[6]  Gregory A. Keoleian,et al.  The application of life cycle assessment to design , 1993 .

[7]  M. Aucott,et al.  Release of Mercury from Broken Fluorescent Bulbs , 2003, Journal of the Air & Waste Management Association.

[8]  S. Ryding ISO 14042 Environmental management • Life cycle assessment • life cycle impact assessment , 1999 .

[9]  Hans-Jürgen Dr. Klüppel,et al.  ISO 14041: Environmental management — life cycle assessment — goal and scope definition — inventory analysis , 1998 .

[10]  C.Stephen Krivanek Mercury control technologies for MWC's: The unanswered questions , 1996 .

[11]  Hans-Jürgen Dr. Klüppel,et al.  The Revision of ISO Standards 14040-3 - ISO 14040: Environmental management – Life cycle assessment – Principles and framework - ISO 14044: Environmental management – Life cycle assessment – Requirements and guidelines , 2005 .

[12]  M. Rabah,et al.  Recovery of aluminium, nickel-copper alloys and salts from spent fluorescent lamps. , 2004, Waste management.

[13]  Jim Petrie,et al.  Process synthesis and optimisation tools for environmental design: methodology and structure , 2000 .