Abstract

PurposeThe purpose of this study was to test the chain-organization environmental footprint (chain-OEF) approach by applying it to part of a pork production chain in Belgium. The approach is supposed to provide insight into the environmental impact of a specific production chain in an efficient manner by applying pragmatic data collection throughout the chain. This is achieved by allocating the environmental impact of each of the production sites to the product of interest using straightforward allocation rules.MethodsThe cradle-to-gate (up to retail) environmental impact of pork was determined by life cycle assessment (LCA), in line with the product and organisation environmental footprint guidelines (PEF and OEF; European Commission 2013b). Foreground data was gathered at a feed production site, two farmers, a slaughterhouse and a meat processing site. All foreground operations are part of the same pork production chain in Belgium. The chain was completed using background data from Ecoinvent v3.01 (Wernet et al. 2016), Agri-Footprint v1.0 (Blonk 2014), European Life Cycle Database v3.0, LCA Food Database (Nielsen et al. 2003) and OEF Sector Rules Retail (Humbert et al. 2015b). The impact was quantified using the international reference life cycle data system (ILCD) midpoint method for 14 impact categories, but focussing on climate change.Results and discussionThe total carbon footprint of the cradle-to-gate pork production system equals 0.46 kg CO2-eq. (100 g pork)−1. This result is quite similar to that of earlier studies analysing the pork production chain: 0.58 and 0.57 kg CO2-eq. (100 g pork)−1 (Bracquené et al. 2011, Agri-Footprint 2014). Most of the carbon footprint was caused by feed production and more specifically, by the feed ingredients and their transport. Grains, soy and palm oil have the largest impact contributions. The farms are responsible for most of the remaining impact. N2O and CH4 emissions are the largest cause of greenhouse gas emissions at the farms. Also, in the other 13 considered impact categories, feed production and farming are responsible for more than half of the total impact, mostly followed by meat processing.ConclusionsApplying the chain-OEF approach in this study has shown that a chain LCA can be performed successfully and pragmatic data collection allows obtaining LCA results relatively fast, especially for small or medium-sized enterprises (SMEs). Whereas data availability was not such an issue, the main bottlenecks identified are data management and the link of LCA to other disciplines such as engineering, policy, etc. which could increase the added value of LCA studies.

Highlights

  • With a growing world population, the demand for a sustainable food supply is increasing (Ilbery and Maye, 2005)

  • Applying the chain-organisation environmental footprint (OEF) approach in this study has shown that a chain life cycle assessment (LCA) can be performed successfully and pragmatic data collection allows obtaining LCA results relatively fast, especially for small or medium-sized enterprises (SMEs)

  • Freshwater eutrophication is mostly caused by emissions during farming (76 %; both feed ingredient production and pig farming) and by the processing of waste meat products originating from the meat processing plant (16 %; the Ecoinvent v3.01 (Wernet et al 2016) scenario assumes mainly incineration)

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Summary

Introduction

With a growing world population, the demand for a sustainable food supply is increasing (Ilbery and Maye, 2005). LCA as defined by ISO 14040/44 is only a framework leaving many methodological choices open This results in differentiation of results for similar products, causes confusion and eases greenwashing. To improve harmonisation and consistency of environmental claims, the European Commission created the Single Market for Green Products Initiative with rules for a product environmental footprint (PEF) and organisation environmental footprint (OEF; European Commission, 2013a, b, c; Galatola and Pant 2014) Apart from these general rules, more stringent standards are defined per product category or per sector during a pilot phase. The initiative aims at lowering the remaining confusion among consumers (TNS Opinion and Social 2014) and to aid producers making reliable green claims It opens the door for more large-scale application of LCA in industry, e.g. for communication or comparisons, and the new standards are welcomed

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