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RESEARCH ARTICLE

Life cycle assessment of greenhouse gas emissions from irrigated maize and their significance in the value chain

Tim Grant A B and Tom Beer A
+ Author Affiliations
- Author Affiliations

A CSIRO Marine and Atmospheric Research, PMB1 Aspendale, Vic. 3195, Australia.

B Corresponding author. Email: timothy.grant@csiro.au

Australian Journal of Experimental Agriculture 48(3) 375-381 https://doi.org/10.1071/EA06099
Submitted: 15 March 2006  Accepted: 6 February 2007   Published: 4 February 2008

Abstract

The life cycle assessment component of this multi-institutional project determined greenhouse gas emissions in pre-farm, on-farm and post-farm activities involved in the use of maize for the manufacture of corn chips. When the emissions were expressed in terms of carbon dioxide-equivalents (CO2-e), pre-farm emissions comprised ~6% of the life cycle emissions, on-farm activities comprised ~36% and post-farm activities accounted for ~58% of life cycle greenhouse gas emissions. We used one 400 g packet of corn chips as the functional unit. The single largest source of greenhouse emissions was the emission of nitrous oxide on the farm as a result of fertiliser application (0.126 kg CO2-e per packet). The next largest was electricity used during the manufacture of the corn chips (0.086 kg CO2-e per packet). The manufacture of the packaging (box plus packet, being 0.06 kg CO2-e) was the next largest source and then the oil for frying the corn chips (0.048 kg CO2-e per packet). Greenhouse gas emissions from fertiliser application were primarily nitrous oxide (N2O), which has a global warming potential of 310 kg CO2-e/kg N2O. In typical irrigated farm systems, these emissions, when converted to CO2-e, are almost three times more than the greenhouse gas emissions that result from energy used to pump water. However, pumping irrigation water from deep bores currently produces greenhouse gas emissions that are almost three times those from irrigation using surface waters. Greenhouse gas emissions from the use of tractors on typical farms are about one-third of the emissions from pumping water. Farm management techniques can be used to increase soil carbon and reduce greenhouse gas emissions. If farms that currently burn stubble were to implement stubble incorporation then, in the absence of other changes to the supply chain, they will achieve a 30% reduction in emissions from ‘cradle to farm-gate’. In absolute terms, when the soil carbon dioxide is included (even though soil carbon dioxide in this instance is not counted as a greenhouse gas in national and international greenhouse gas inventories), our measurements indicate that carbon dioxide and greenhouse gas emissions from farms that produce maize using stubble incorporation are 56% lower than emissions from farms that burn their stubble. The pre-farm and on-farm operations add $0.40 value per kg of CO2-e greenhouse gas emitted. Post-farm processing added $2 value per kg of CO2-e greenhouse gas emitted. Processing maize for corn chips emitted more greenhouse gases than processing the same amount of corn for starch or ethanol.


Acknowledgements

We acknowledge the financial support of the Australian Greenhouse Office, The Grains Research and Development Corporation and the CRC for Greenhouse Accounting. We also acknowledge the work of the whole project team that consisted of Dr Tom Beer, Dr Mick Meyer and Mr Tim Grant from CSIRO Marine and Atmospheric Research; Mr Kim Russell from PEAQ Management; Mr Clive Kirkby, Ms Alison Fattore, and Mr David Smith from CSIRO Land and Water; and Dr Deli Chen and Dr Robert Edis from the University of Melbourne.


References


ABARE (2002) ‘Australian commodity statistics: petroleum.’ (Australian Bureau of Agricultural Research Economics: Canberra)

AGO (2005) ‘National greenhouse gas inventory 2003.’ National Greenhouse Gas Inventory Committee. (Australian Greenhouse Office: Canberra)

Apelbaum Consulting Group (2001) ‘Australian transport facts, 2001.’ (Apelbaum Consulting Group: Blackburn, Vic.)

Beer T, Grant T, Morgan G, Lapszewicz J, Anyon P, Edwards J, Nelson P, Watson H, Williams D (2001) Comparison of transport fuels. Report EV45A/2/F3C to the Australian Greenhouse Office. CSIRO Atmospheric Research. (Australian Greenhouse Office: Canberra) Available at www.greenhouse.gov.au/transport/comparison [Verified 27 November 2007]

Beer T, Meyer M, Grant T, Russell K, Kirkby C, et al. (2005) Life-cycle assessment of greenhouse gas emissions from agriculture in relation to marketing and regional development – irrigated maize: from maize field to grocery store. Final Report HQ06A/6/F3.5. CSIRO Division of Marine and Atmospheric Research.

Consoli F (1993) ‘Guidelines for life cycle assessment: a code of practice.’ (Society of Environmental Toxicology and Chemistry (SETAC): Pensacola, FL)

Duxbury JM (2005) Soil carbon sequestration and nitrogen management for greenhouse gas mitigation. In ‘Climate change and agriculture: promoting practical and profitable responses’. pp. IV-5–IV-7. Available at www.climateandfarming.org/pdfs/FactSheets/IV.2Soil.pdf [Verified 27 November 2007]

Eckard R (2006) Are there win-win strategies for minimising greenhouse gas emissions from agriculture? In ‘Proceedings of OUTLOOK 2006’. pp. 1–9. (Australian Bureau of Agricultural and Resource Economics: Canberra)

Edis RB, Chen D, Wang G, Turner DA, Park K, Meyer M, Kirkby C (2008) Soil nitrogen dynamics in irrigated maize systems as impacted on by nitrogen and stubble management. Australian Journal of Experimental Agriculture 48, 382–386.
CAS |
[Verified 27 November 2007]

Grant T, James K, Partl H (2003) Life cycle assessment of waste and resource recovery options (including energy from waste). Final Report for EcoRecycle Victoria. Centre for Design, RMIT University, Melbourne, Victoria. Available at www.cfd.rmit.edu.au/programs/life_cycle_assessment [Verified 27 November 2007]

Hansson P-A, Mattsson B (1999) Influence of derived operation-specific tractor emission data on results from an LCI on wheat production. International Journal of Lifecycle Assessment 4(4), 202–206.
CAS |
[Verified 27 November 2007]

Queensland Department of Natural Resources and Water (2006) NRM facts – phosphate rock. http://www.nrw.qld.gov.au/factsheets/pdf/mines/m4.pdf [Website no longer available]

Tilman D, Cassman KG, Matson PA, Naylor R, Polasky S (2002) Agricultural sustainability and intensive production practices Nature 418, 671–677.
Crossref | GoogleScholarGoogle Scholar | CAS | PubMed | [Verified 29 November 2007]

West TO, Marland G (2002) A synthesis of carbon sequestration, carbon emissions, and net carbon flux in agriculture: comparing tillage practices in the United States. Agriculture Ecosystems & Environment 91, 217–232.
Crossref | GoogleScholarGoogle Scholar | open url image1

West TO, Post WM (2002) Soil organic carbon sequestration rates by tillage and crop rotation: a global data analysis. Soil Science Society of America Journal 66, 1930–1946.
CAS |
open url image1