The price of protein: Review of land use and carbon footprints from life cycle assessments of animal food products and their substitutes
Highlights
► 104 Carbon footprints and 43 land footprints of protein sources are examined. ► Very large differences in impact between protein sources were found. ► In the life cycles, in general, the farm phase is the most important. ► Vegetal sources, poultry products and certain seafood have low carbon footprints. ► Ruminant meat and some types of seafood have high carbon footprints.
Introduction
The role of animal husbandry in climate change and loss of biodiversity has been highlighted in several studies in the past decade (e.g. Kramer, 2000, Steinfeld et al., 2006, Garnett, 2008, FAO, 2009). These publications provide the larger picture of the impacts of livestock production on a global scale. More focus and detail can be found in environmental life cycle assessment (LCA) studies of animal food products, many of which were also published the past few years.
In an LCA the environmental impacts of a product is quantified as much as possible in a consistent and standardized way. De Vries and De Boer (2010) have reviewed a selection of LCA studies on animal products. Other meta-publications on LCAs of food products include Yan et al. (2011), Roy et al., 2009, Flachowsky and Hachenberg, 2009 and González et al. (2011). These publications mainly focus on greenhouse gases and carbon labelling, or include a limited group of products or a limited number of studies. The present review presents a broader view, based on the analysis of 52 LCA studies on meat, milk, seafood and other sources of protein. The goals were to:
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Identify the ranges in land requirements and carbon footprints of different sources of protein.
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Identify the most important inputs and processes in the life cycles.
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Identify what are the main causes of differences.
We focused on land use (occupation) and greenhouse gas emissions because these aspects are very relevant to damage to ecosystems and consequential global loss of biodiversity (Alkemade et al., 2009, Rockstrom et al., 2009).
Section snippets
Methods
A method commonly used to analyse the environmental impacts of products is the environmental life cycle assessment (LCA). It is an internationally recognized method, and the ISO standards (ISO 14040 and 14044) provide guidelines for conducting LCAs. They can be used to identify the most important contributors in a production chain (gravity analysis or contribution analysis), or to make a systematic comparison of different products or production methods. Many different environmental impact
Results
The next two sections present the land use and carbon footprints of the various food products, according to the LCA studies. Tables and graphs only present results for conventional production, with the exception of the results for eggs from free range production from Mollenhorst et al. (2006), as this represents a large part of the consumer market in Europe.
Trade-offs and rebounds
This review covers the carbon footprints and land use of the major protein-rich products in the western diet. Cereals are also a significant supplier of protein, but are not included. On the basis of differences in environmental impact of the various products, we conclude that there is a large potential for reductions in the environmental impact of food consumption by choosing low-impact sources of protein. However, large scale shifts may have rebounds or trade-offs. The impact of such shifts
Conclusions
In general, from an analysis of life cycle assessment studies, it can be concluded that food products of animal origin have higher climate- and land use related impacts than vegetable products. Meat substitutes containing egg protein, poultry, eggs and some seafood products also show small carbon footprints. The largest impacts per kilogram of product was found for ruminant meat, both in terms of greenhouse gas emissions and in terms of land use (occupation). Pork has intermediate impacts.
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