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LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

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GROUP 2, SESSION A: CARBON OR WATER FOOTPRINTS, SOIL, BIODIVERSITY 8 th Int. Conference on <strong>LCA</strong> <strong>in</strong> the<br />

Agri-<strong>Food</strong> Sector, 1-4 Oct <strong>2012</strong><br />

55. Us<strong>in</strong>g <strong>LCA</strong> to <strong>in</strong>form policy for biochar <strong>in</strong> New Zealand<br />

Ruy Anaya de la Rosa 1 , Sarah J. McLaren 1,2,* , Jim Jones 1 , Ralph Sims 1<br />

1 Massey University, Palmerston North, New Zealand, 2 New Zealand Life Cycle Management Centre, New<br />

Zealand, Correspond<strong>in</strong>g author. E-mail: S.McLaren@massey.ac.nz<br />

Biochar is carbonised biomass; the focus of this study is biochar obta<strong>in</strong>ed from susta<strong>in</strong>able sources and sequestered<br />

<strong>in</strong> soils to susta<strong>in</strong>ably enhance their agricultural and environmental value under present and future<br />

management. Biochar has attracted <strong>in</strong>ternational attention as a carbon sequestration strategy s<strong>in</strong>ce it can take<br />

hundreds or thousands of years to decompose. Moreover, biochar offers opportunities <strong>in</strong> the energy, soil<br />

management, and end-of-life biomass (ELB) recycl<strong>in</strong>g sectors.<br />

The quantity of ELB feedstocks <strong>in</strong> New Zealand that could potentially be used to produce biochar was assessed.<br />

In a highly optimistic scenario <strong>in</strong> which 80% of the available ELB is sourced to make biochar, over 1<br />

million tonnes of CO2 could potentially be sequestered every year. This translates to about 1.5% of NZ’s<br />

total greenhouse gas emissions (based on 2009 data). Although this percentage is small, the relative contribution<br />

of us<strong>in</strong>g biochar on n<strong>et</strong> greenhouse gas emissions may be much more significant when consider<strong>in</strong>g<br />

products <strong>in</strong> particular economic sectors from a life cycle perspective e.g., <strong>in</strong> d<strong>et</strong>erm<strong>in</strong><strong>in</strong>g the carbon footpr<strong>in</strong>t<br />

of agricultural products.<br />

Although a number of biochar systems have been evaluated from a life cycle perspective, only two studies<br />

(Roberts <strong>et</strong> al. 2010; Hammond <strong>et</strong> al., 2010) and one life cycle <strong>in</strong>ventory analysis (Kameyama <strong>et</strong> al., 2010)<br />

seem to have followed <strong>LCA</strong> m<strong>et</strong>hodology – and they all focus on just one impact category (climate change).<br />

Also, one <strong>LCA</strong> study of <strong>et</strong>hanol produced from a hectare of corn <strong>in</strong>cludes stover-derived biochar <strong>in</strong> the<br />

analysis (Kauffman <strong>et</strong> al., 2011). Us<strong>in</strong>g an <strong>LCA</strong> approach, the m<strong>et</strong>hodological issues concern the goal, scope<br />

and decision-context of the study; functional unit; multiple functions; system boundaries and allocation;<br />

choice of impact categories; <strong>in</strong>direct consequences; and reference scenario with which the biochar system is<br />

compared. At the forefront of these variables, it is not clear when and how to conduct attributional versus<br />

consequential <strong>LCA</strong>, and so results can vary considerably.<br />

Therefore, particularly when consider<strong>in</strong>g future policy options to encourage or discourage production and<br />

use of biochar, it is important to carefully consider the different variables and their <strong>in</strong>fluence on the f<strong>in</strong>al<br />

results of an <strong>LCA</strong> study of biochar. This paper presents the results of a life cycle study on three different<br />

future management options for the woody ELB from apple orchards <strong>in</strong> the Hawke’s Bay region <strong>in</strong> NZ undertaken<br />

with the goal of <strong>in</strong>form<strong>in</strong>g stakeholders and policy makers on the best use of biomass to mitigate climate<br />

change. Three different scenarios are compared: i) reference scenario, <strong>in</strong> which the woody ELB is<br />

mulched and left on orchard soils; ii) energy scenario, <strong>in</strong> which the ELB is used for energy generation; and<br />

iii) biochar scenario, <strong>in</strong> which the ELB is used for biochar production and application <strong>in</strong>to the same area. The<br />

results show that the fuller trade-offs associated with alternative end uses of biomass need to be explored<br />

us<strong>in</strong>g a more compl<strong>et</strong>e system expansion perspective and representation of alternatives.<br />

References<br />

Hammond, J., Shackley, S., Sohi, S., Brownsort, P., 2011. Prospective life cycle carbon abatement for pyrolysis<br />

biochar systems <strong>in</strong> the UK. Energy Policy, 39, 2646-2655.<br />

Kameyama, K., Sh<strong>in</strong>ogi, Y., Miyamoto, T., Agarie, K., 2010. Estimation of n<strong>et</strong> carbon sequestration potential<br />

with farmland application of bagasse charcoal: life cycle <strong>in</strong>ventory analysis through a pilot sugarcane<br />

bagasse carbonisation plant. Aust. J Soil Res.,48, 586-592.<br />

Kauffman, N., Hayes, D., Brown, B., 2011. A life cycle assessment of advanced biofuel production from a<br />

hectare of corn. Fuel, 90,3306-3314.<br />

Roberts, K.G., Gloy, B.A., Joseph, S., Scott, N.R., & Lehmann, J., 2010. Life Cycle Assessment of biochar<br />

systems: estimat<strong>in</strong>g the energ<strong>et</strong>ic, economic, and climate change potential. Environ. Sci. Tech., 44, 827-<br />

833.<br />

735

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