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RESEARCH ARTICLE

Greenhouse gas and energy balance of dairy farms using unutilised pasture co-digested with effluent for biogas production

Mark Lieffering A C , Paul Newton A and Jürgen H. Thiele B
+ Author Affiliations
- Author Affiliations

A AgResearch Grasslands, Private Bag 11008, Palmerston North, New Zealand.

B Waste Solutions Ltd, PO Box 997, Dunedin, New Zealand.

C Corresponding author. Email: mark.lieffering@agresearch.co.nz

Australian Journal of Experimental Agriculture 48(2) 104-108 https://doi.org/10.1071/EA07252
Submitted: 7 August 2007  Accepted: 15 November 2007   Published: 2 January 2008

Abstract

Greenhouse gas (GHG) emissions from New Zealand dairy farms are significant, representing nearly 35% of New Zealand’s total agricultural emissions. Although there is an urgent need for New Zealand to reduce agricultural GHG emissions in order to meet its Kyoto Protocol obligations, there are, as yet, few viable options for reducing farming related emissions while maintaining productivity. In addition to GHG emissions, dairy farms are also the source of other emissions, most importantly effluent from milking sheds and feed pads. It has been suggested that anaerobic digestion for biogas and energy production could be used to deal more effectively with dairy effluent while at the same time addressing concerns about farm energy supply. Dairy farms have a high demand for electricity, with a 300-cow farm consuming nearly 40 000 kWh per year. However, because only ~10% of the manure produced by the cows can be collected (e.g. primarily at milking times), a maximum of only ~16 000 kWh of electricity per year can be produced from the effluent alone. This means that anaerobic digestion/electricity generation schemes are currently economic only for farms with more than 1000 cows. A solution for smaller farms is to co-digest the effluent with unutilised pasture sourced on the farm, thereby increasing biogas production and making the system economically viable. A possible source of unutilised grass is the residual pasture left by the cows immediately after grazing. This residual can be substantial in the spring–early summer, when cow numbers (demand) can be less than the pasture growth rates (supply). The cutting of ungrazed grass (topping) is also a useful management tool that has been shown to increase pasture quality and milk production, especially over the late spring–summer. In this paper, we compare the energy and GHG balances of a conventional farm using a lagoon effluent system to one using anaerobic digestion supplemented by unutilised pasture collected by topping to treat effluent and generate electricity. For a hypothetical 300-cow, 100-ha farm, topping all paddocks from 1800 to 1600 kg DM/ha four times per year over the spring–summer would result in 80 tonnes of DM being collected, which when digested to biogas would yield 50 000 kWh (180 GJ) of electricity. This is in addition to the 16 000 kWh from the effluent digestion. About 90 GJ of diesel would be used to carry out the topping, emitting ~0.06 t CO2e/ha. In contrast, the anaerobic/topping system would offset/avoid 0.74 t CO2e/ha of GHG emissions: 0.6 t CO2e/ha of avoided CH4 emissions from the lagoon and 0.14 t CO2e/ha from biogas electricity offsetting grid electricity GHGs. For the average dairy farm, the net reduction in emissions of 0.68 CO2e/ha would equate to nearly 14% of the direct and indirect emissions from farming activities and if implemented on a national scale, could decrease GHG emissions nearly 1.4 million t CO2e or ~10% of New Zealand’s Kyoto Protocol obligations while at the same time better manage dairy farm effluent, enhance on-farm and national energy security and increase milk production through better quality pastures.


References


Amon T, Amon B, Kryvoruchko V, Machmuller A, Hopfner-Sixt K , et al. (2007) Methane production through anaerobic digestion of various energy crops grown in sustainable crop rotations. Bioresource Technology 98, 3204–3212.
Crossref | GoogleScholarGoogle Scholar | CAS | PubMed | [Verified 18 November 2007].

Chaves AV, Burke JL, Waghorn GC, Brookes IM (2006) Digestion kinetics of leaf, stem and inflorescence from five species of mature grasses. Journal of the Science of Food and Agriculture 86, 816–825.
Crossref | GoogleScholarGoogle Scholar | CAS | [Verified 18 November 2007].

Covec (2006) ‘Heavy industry energy demand.’ Report prepared for the Ministry of Economic Development. Available at http://www.covec.co.nz/pdf/heavy-industry-energy-demand.pdf [Verified 19 November 2007].

Craggs R (2004) Potential for biogas recovery from anaerobic ponds in New Zealand. In ‘Bioenergy association of New Zealand workshop on biogas technology – update and opportunities in NZ, Christchurch’. Available at http://www.bioenergy.org.nz/documents/7_Potential%20for%20biogas%20recovery%20from%20anaerobic%20ponds%20in%20NZ.pdf [Verified 19 November 2007].

EFNZ (2005) ‘Energy efficient ways to improve the economic bottom line of your dairy farm.’ (Energy Federation of New Zealand Inc.: Wellington, NZ)

Flemmer CL , Flemmer RC , McDonald CW , Archer RH , Cleland DJ (2005) An assessment of the ecological impact of the New Zealand dairy farming sector. In ‘Proceedings of the ANZSEE conference, Palmerston North, New Zealand’. pp. 73–84.

Fleming P.H. (2003) ‘Farm technical manual.’ (Lincoln University: NZ)

IPCC (2006) Emissions from livestock and manure management. In ‘2006 IPCC guidelines for national greenhouse gas inventories. Agriculture, forestry and other land use. Vol. 4’.

Kolver ES , Penno J , Macdonald K , McGrath J , Carter W (1999) Mowing pasture to improve milk production. In ‘Proceeding of the Ruakura dairy farmers’ conference. Vol. 51’. pp. 95–96.

MAF (2003) ‘Contribution of the land-based primary industries to New Zealand’s economic growth.’ (New Zealand Ministry of Agriculture and Forestry: Wellington)

MED (2006) ‘New Zealand’s energy outlook to 2030.’ (Ministry of Economic Development: Wellington)

MED (2007) ‘New Zealand energy greenhouse gas emissions 1990–2006.’ (Ministry of Economic Development: Wellington)

MfE (2007 a) ‘New Zealand’s greenhouse gas inventory 1990–2005: an overview.’ Reference ME 806. (New Zealand Ministry for the Environment: Wellington) Available at http://www.mfe.govt.nz/publications/climate/nir-jul07/index.html [Verified 18 November 2007].

MfE (2007 b) ‘New Zealand greenhouse gas inventory 1990–2005: an overview.’ Reference ME 811. (New Zealand Ministry for the Environment: Wellington) Available at http://www.mfe.govt.nz/publications/climate/nir-jul07/index.html [Verified 18 November 2007].

PGGRC (2004) A pastoral greenhouse gas research strategy: annual report to the Crown on progress for the year ended 30 June 2004. Pastoral Greenhouse Gas Research Consortium.

Yan T , Mayne CS , Porter MG (2006) Effects of dietary and animal factors on methane production in dairy cows offered grass silage-based diets. In ‘Proceedings of the 2nd international conference on greenhouse gases and animal agriculture: an update’. International Congress Series. Vol. 1293. pp. 123–126.