Global warming potential associated with dairy products in the Republic of Ireland
Introduction
With the world's population growing at a rate of over 1% per year, there is a constantly increasing demand for food. In 2015, the milk quota system that is in place in Europe is to be abolished, with an increase in milk production expected. However, if the European Union is to meet its climate and energy targets for 2020 of a 20% increase in energy efficiency and a 20% reduction in greenhouse gas (GHG) emissions (EU, 2008), the dairy industry must strive to reduce impacts and increase sustainability to deal with this expected increase in milk production.
Ireland is one of Europe's largest producers of cows' milk with an annual production of over 5 billion litres (CSO, 2014) (Fig. 1). Currently, dairy ingredients and products comprise of almost 30% of the Irish food and drink export market.In 2013, dairy ingredients and products surpassed €3 billion for the first time, making it Ireland's largest indigenous industry (National Milk Agency, 2014). Approximately 10% of Ireland's milk is used for liquid milk consumption with the remainder made into a variety of products, including butter, cheese, milk powder, whey derivatives and proteins. The production values for dairy products manufactured in the Republic of Ireland in 2012 are given in Table 1.
Currently, the Republic of Ireland is on the brink of a new era for the dairy industry as quotas, which restrict milk production, are being abolished in 2015. As a result, milk production is expected to increase by 50% by 2020 (Farrelly et al., 2014). This increase in the volume of milk being processed, together with stringent measures on emissions from the industry and growing commercial drive for operational efficiencies, is driving the need for innovative technological and operational solutions within the dairy processing industry. Life cycle assessment (LCA) provides a useful tool for estimating the greenhouse gas emissions associated with a particular product or service. In addition, the main contributors to these emissions are highlighted within the analysis and its interpretation (for example, specific energy or resource consumption).
Summaries of the findings from a large number of LCAs performed in order to estimate the global warming potential (GWP) of raw milk production worldwide are available in previously published literature. For example, Crosson et al. (2011) undertook a review of whole farm system models used in quantifying the greenhouse gas emissions relating to beef and dairy production. Yan et al. (2011) completed a review on milk and dairy production in a European context. Milani et al., 2011, Hagemann et al., 2011 and Fantin et al. (2012) have compiled a summary of the GWP of milk production from a large number of studies performed worldwide. These authors found that, typically, the GWP of milk production is between 0.8 and 1.4 kg CO2eq kg−1 milk at the farm gate, where CO2eq is carbon dioxide equivalent, which takes account of the GWP of greenhouse gases (carbon dioxide (CO2), nitrogen oxide (N2O) and methane (CH4)) according to the weighting given by the IPCC (2007) guidelines for a time horizon of 100 years (i.e. GWPs of CO2, N2O and CH4 are 1, 298 and 25, respectively). With regard to the Irish dairy sector, Casey and Holden (2005) have presented the carbon footprint for an average dairy farm unit. They found that the GWP of milk production in Ireland for the years between 1997 and 2001, for an economic allocation, between dairy, meat and crops production, was 1.3 kg CO2eq kg−1 energy corrected milk (ECM) at the farm gate, where energy corrected milk (ECM) is defined as (Sjaunja et al., 1990):
However, Casey and Holden (2005) note that the value of the GWP estimated is affected by the method of allocation employed (no allocation, mass allocation or economic allocation) and the value varied between 1.3 and 1.5 kg CO2eq kg−1 ECM. O'Brien et al. (2012) compares two research farms in order to explore the effects of seasonal grass-based and confinement dairy farms on GHG emissions. For seasonal grass-based dairy farms, which are the most common type of farm used in Ireland, the GHG emissions were found to be 0.8743 kg CO2eq kg−1 fat and protein corrected milk (FPCM) at the farm gate, where FPCM is given by the formula:
Additionally, O'Brien et al. (2014) estimated the carbon footprint of milk production on grass-based farms to be 1.11 kg CO2eq kg−1 FPCM, which varied from 0.87 to 1.72 kg CO2eq kg−1 FPCM, using data collected from 171 commercial Irish dairy farms. Upton et al. (2013) investigated the energy consumption on dairy farms in Ireland using a case study of 22 commercial dairy farms for 2011. The average energy consumption was found to be 2.37 MJ per kg of energy corrected milk at the farm gate. Furthermore, Murphy et al. (2014) explored the direct water use on 25 Irish dairy farms and found that approximately 6.4 L of water is used for every L of milk produced.
LCA has been used in studies of many major manufacturing countries of dairy products in order to evaluate the environmental and socio-economic impacts of the industry and its products. These countries include the USA (Kim et al., 2013, Nutter et al., 2013, Thoma et al., 2013), New Zealand (Flysjo, 2012), Canada (Vergé et al., 2013), Serbia (Djekic et al., 2014) and Portugal (González-García et al., 2012, González-García et al., 2013c, González-García et al., 2013b). Furthermore, Geraghty (2011) undertook a study in order to benchmark resource efficiency in Ireland's dairy processing sector. In this study, the energy and overall water consumption in 2009 of 15 dairy processing plants, that combined made up 94% of the dairy processing sector, was analysed. For the Irish dairy sector, the overall water consumption in dairy processing plants was estimated as 2.5 L per L of milk processed. A summary of studies published in the literature relating to environmental impacts of dairy processing plants is presented in Table 2. This builds on the summary presented by Djekic et al. (2014) for the dairy sector, but only presents studies relating to the processing of dairy products. Previously, the GWP associated the production and manufacture of dairy products in Ireland has not been assessed. Furthermore, the direct energy and overall water consumption associated with processing fluid milk has not been assessed, as it was omitted from the study performed by Geraghty (2011).
The purpose of the study is to examine the GWP of the dairy industry in the Republic of Ireland on a macro-scale using LCA. Raw milk production, raw milk transportation and dairy processing are the phases examined in this study. Previously no assessment of processed fluid milk and only an assessment of energy use and water consumption for selected dairy products were available for the dairy processing industry in the Republic of Ireland. The GWP attributable to each phase, as well as the total GWP of these phases, are presented for each dairy product manufactured. As a result of data availability on energy usage and sources in the dairy processing plants, a breakdown on direct energy usage and direct water consumption for the dairy processing industry in the Republic of Ireland is presented. The results of this macro study of the industry will identify the major contributors to GWP within the Irish dairy sector.
Section snippets
Materials and methods
This study has been structured in accordance with the life cycle assessment guidelines of the International Organisation for Standardisation (ISO): ISO 14040 (ISO, 2006a) and ISO 14044 (ISO, 2006b). Furthermore, particular attention was paid to the LCA methodology for the dairy industry published by the International Dairy Federation (2010). The International Dairy Federation's LCA methodology encompasses a number of existing standards and guidelines, including ISO 14040 (ISO, 2006a), ISO 14044
Global warming potential associated with raw milk production
A number of changes to the model developed by Casey and Holden (2005) were implemented in order to accurately determine the GWP associated with raw milk production in the Republic of Ireland, circa 2012, which are discussed in Section 2.6. The GWP associated with raw milk production for an average Irish dairy farm unit, circa 2012, is estimated to be 1.17 kg CO2eq kg−1 FPCM, using economic allocation, at the farm gate. This result is in line with the results of O'Brien et al. (2014), which
Conclusion
In this paper, a macro-scale environmental life cycle assessment of the Irish dairy industry is performed. The analysis is broken into three phases (raw milk production, raw milk transportation and processing) for 11 dairy products. Previously, the GWP associated the production and manufacture of dairy products in Ireland has not been assessed. The results of this study will serve as a benchmark for the Irish dairy industry as individual producers and processers can evaluate and compare their
Acknowledgments
The authors would like to acknowledge the funding provided by the Department of Agriculture, Food and the Marine for the DairyWater project (Ref.: 13-F-507); for additional details: www.dairywater.ie. The second author would also like to acknowledge the support of Science Foundation Ireland through the Career Development Award programme (Grant No. 13/CDA/2200). The authors would also like to express their gratitude to the anonymous reviewers of this paper for their constructive comments.
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