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How does co-product handling affect the carbon footprint of milk? Case study of milk production in New Zealand and Sweden

  • CARBON FOOTPRINTING
  • Published:
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Abstract

Purpose

This paper investigates different methodologies of handling co-products in life cycle assessment (LCA) or carbon footprint (CF) studies. Co-product handling can have a significant effect on final LCA/CF results, and although there are guidelines on the preferred order for different methods for handling co-products, no agreed understanding on applicable methods is available. In the present study, the greenhouse gases (GHG) associated with the production of 1 kg of energy-corrected milk (ECM) at farm gate is investigated considering co-product handling.

Materials and methods

Two different milk production systems were used as case studies in the investigation of the effect of applying different methodologies in co-product handling: (1) outdoor grazing system in New Zealand and (2) mainly indoor housing system with a pronounced share of concentrate feed in Sweden. Since the cows produce milk, meat (when slaughtered), calves, manure, hides, etc., the environmental burden (here GHG emissions) must be distributed between these outputs (in the present study no emissions are attributed to hides specifically, or to manure which is recycled on-farm). Different methodologically approaches, (1) system expansion (two cases), (2) physical causality allocation, (3) economic allocation, (4) protein allocation and (5) mass allocation, are applied in the study.

Results and discussion

The results show large differences in the final CF number depending on which methodology has been used for accounting co-products. Most evident is that system expansion gives a lower CF for milk than allocation methods. System expansion resulted in 63–76% of GHG emissions attributed directly to milk, while allocation resulted in 85–98%. It is stressed that meat is an important by-product from milk production and that milk and beef production is closely interlinked and therefore needs to be considered in an integrated approach.

Conclusions

To obtain valid LCA/CF numbers for milk, it is crucial to account for by-products. Moreover, if CF numbers for milk need to be compared, the same allocation procedure should be applied.

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Notes

  1. CF is a term used to describe the total amount of greenhouse gas (GHG) emissions of a process or a product system to indicate their contribution to climate change. It also includes emissions of methane and nitrous oxide, which are of special importance for agricultural products.

  2. The milk quota system in EU will end in 2015.

  3. Manure and hides are also outputs, but all manure is here assumed to stay within the system boundaries (i.e. the dairy system), and hides are assumed to be of minor importance and are generally accounted for within the beef component.

  4. The Product Category Rule (PCR) for processed liquid milk states that meat from slaughtered cows and calves “shall be omitted considering that the useful meat (kg) is negligible” (Swedish Environmental Management Council, 2010), which is here interpreted as 100% of emissions shall be allocated to milk and none to meat. In the former PCR for milk and milk-based products (Swedish Environmental Management Council, 2006), mass allocation was recommended.

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Acknowledgements

The authors gratefully acknowledge the help from Mark Boyes (AgResearch, New Zealand). The study was performed with funding from the Danish Agency for Science, Technology and Innovation.

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Correspondence to Anna Flysjö.

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Flysjö, A., Cederberg, C., Henriksson, M. et al. How does co-product handling affect the carbon footprint of milk? Case study of milk production in New Zealand and Sweden. Int J Life Cycle Assess 16, 420–430 (2011). https://doi.org/10.1007/s11367-011-0283-9

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  • DOI: https://doi.org/10.1007/s11367-011-0283-9

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