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Life Cycle Assessment in the Cereal and Derived Products Sector

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Abstract

This chapter discusses the application of life cycle assessment methodologies to rice, wheat, corn and some of their derived products. Cereal product systems are vital for the production of commodities of worldwide importance that entail particular environmental hot spots originating from their widespread use and from their particular nature. It is thus important for tools such as life cycle assessment (LCA) to be tailored to such cereal systems in order to be used as a means of identifying the negative environmental effects of cereal products and highlighting possible pathways to overall environmental improvement in such systems. Following a brief introduction to the cereal sector and supply chain, this chapter reviews some of the current cereal-based life cycle thinking literature, with a particular emphasis on LCA. Next, an analysis of the LCA methodological issues emerging from the literature review is carried out. The following section of the chapter discusses some practices and approaches that should be considered when performing cereal-based LCAs in order to achieve the best possible results. Conclusions are drawn in the final part of the chapter and some indications are given of the main hot spots in the cereal supply chain.

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Notes

  1. 1.

    ‘The total burdens of producing grain and straw are: \(\text{T}=\text{H}+(1-{{p}_{s}})I+{{p}_{s}}\text{B}+{}\text{ D}\)$.$ Then the burden allocated to grain is: \({{\text{G}}^{\text{* }{}}}=(\text{H}+\text{I})({{\text{Y}}_{\text{g}}}/{{\text{Y}}_{\text{g}}}+{{\text{v}}_{\text{s}}}{{\text{p}}_{\text{s}}}{{\text{Y}}_{\text{s}}})+\text{D}\), and the burden allocated to straw is: \({{\text{S}}^{\text{* }{}}}=((\text{H}+\text{I})({{\text{v}}_{\text{s}}}{{\text{p}}_{\text{s}}}{{\text{Y}}_{\text{s}}}))\text{/(}({{\text{Y}}_{\text{g}}}+{{\text{v}}_{\text{s}}}{{\text{p}}_{\text{s}}}{{\text{Y}}_{\text{s}}}))+{{\text{p}}_{\text{s}}}(\text{B}-\text{I})\) where H is the vector of burdens of producing grain up to the end of combine harvesting per hectare, I is the vector of burdens of chopping for incorporation for all straw produced, D is the vector of burdens of drying and storage of grain, B is the vector of straw baling burdens for all straw produced, ${{\text{p}}_{\text{s}}}$ is the proportion of straw baled and harvested, ${{\text{Y}}_{\text{g}}}$ is the net yield of grain per hectare at standard DM content, ${{\text{Y}}_{\text{s}}}$ is the yield of straw per hectare (whether harvested or not) at standard DM content, and ${{\text{v}}_{\text{s}}}$ is the relative value of the straw prior to baling versus the grain, typically 0.05’ (Williams et al. 2010

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Conclusions

Conclusions

Cereals and their derived products represent agricultural commodities of worldwide importance, with particular environmental hot spots originating from their widespread use and from their particular nature. The review illustrated in this chapter of the life cycle approaches related to cereals has highlighted that the agricultural phase is in most cases the one responsible for a larger share of the impacts of such product systems. Specifically, fertiliser and pesticide production and use and fuel-related emissions seem to be a common source of impact. Fuel use is responsible for a large contribution to the energy demand and acidification. Fertilisation and pesticide usage are also responsible for a large quota of the overall energy use during the life cycle of cereal-based products and hence are also responsible for the production of GHG. Such energy demand, together with ozone-depleting and acidifying emissions typical of intensive agricultural systems, are the reason for the lower impact of alternative organic types of cultivation that generally do not involve the use of pesticides and avoid the production of fertilisers, including nitrogen-based ones. However, even though organic agricultural approaches can potentially lower the overall impact of cropping systems, the lower fertiliser use and relative energy use in such systems can at times be counterbalanced by larger energy use for fieldwork and lower yields, which in turn lead to overall greater land occupation needed for the cereal production.

The growing number of CF studies highlights an emphasis on the study of the effects of cereal systems on climate change. In this context, rice differentiates itself from corn and wheat since there are many types of rice and production processes, all of which are responsible not only for the above-mentioned major contributions deriving from the production and use of fertilisers but also for the contribution of methanogenesis occurring in the waterlogged soil. Accordingly, there still seems to be no unique methodology for the reduction of the impacts of crop production, and the results from the studies vary substantially; however, the literature indicates that careful use of organic approaches and controlled water use and puddling methods need to be considered in order to reduce both WFs and CFs. What can certainly improve the overall sustainability of cereal production is the use of correct crop rotation by following the cereal cultivation, whenever possible, with legume or vegetable cultivation.

The literature review has also highlighted that the user behaviour when dealing with cereal-based products, for example in terms of transport distance and typology for the purchase of such products or the disposal of waste, can heavily influence the overall environmental sustainability of such product systems. There is thus a need to inform customers better and enhance their awareness of the possibilities of contributing to more sustainable cereal product systems with particular reference to the end of life of the product, which is often one of the least-studied LCA phases.

Overall, the implementation of LCA approaches, at an institutional level (both in developed and in developing countries), at the large corporate firm and SME levels, has increased the environmental consciousness of the people involved in the cereal sector, including users and customers, with an overall reduction of the burdens deriving from such product systems. There is in fact growing use of LCA in the cereal sector for the obtaining of environmental labels (e.g. EPDs). However, there is still a need for a better understanding of the difficulties that can be encountered when performing an LCA of a cereal product system in order to gain the best possible results, which can be used to improve the sustainability of the system. Some of these methodological aspects have been discussed in this chapter, such as the site and time dependency of pesticide diffusion modelling, the need for a deeper analysis and a standardised methodology for calculating the effects of land use on the quality of soil and biodiversity and the need for better quantification and qualification of water use. Among the reviewed studies, the system boundary and functional unit definition appear to be critical stages of the LCAs, in which it may be necessary to use one or more FUs, inevitably using allocation for environmental burden partitioning, and in which certain assumptions have to be made in order to progress with the overall assessment and overcome the lack of data and time or cost issues. The sources of information at the base of these assumptions are not always accurate; hence, it is important to explicate them carefully and evaluate the representativeness of the results and their variability in order to produce useful cereal LCA work that can help understand and improve the sustainability of such product systems.

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Renzulli, P. et al. (2015). Life Cycle Assessment in the Cereal and Derived Products Sector. In: Notarnicola, B., Salomone, R., Petti, L., Renzulli, P., Roma, R., Cerutti, A. (eds) Life Cycle Assessment in the Agri-food Sector. Springer, Cham. https://doi.org/10.1007/978-3-319-11940-3_4

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