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

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

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GROUP 4, SESSION B: CROP PRODUCTION SYSTEMS 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 />

116. A life cycle assessment of rice cultivation<br />

Torsten Rehl 1, , Barbara Dannenmann 2 , Sab<strong>in</strong>e Deiml<strong>in</strong>g 1 , Joachim Müller 2<br />

1 PE INTERNATIONAL AG, Le<strong>in</strong>felden-Echterd<strong>in</strong>gen, Germany, 2 University of Hohenheim, Institute of<br />

Agricultural Eng<strong>in</strong>eer<strong>in</strong>g (440), Stuttgart, Germany, Correspond<strong>in</strong>g author. E-mail: t.rehl@pe<strong>in</strong>ternational.com<br />

Rice cultivation represented about 22% of the world´s gra<strong>in</strong> crops area <strong>in</strong> 2008 (FAO 2010). It is cultivated<br />

across a vast area spann<strong>in</strong>g wide ranges of temperate, subtropical and tropical climates. Various climatic and<br />

socio-economic conditions at different locations effect the rice cultivation and the environmental impacts<br />

go<strong>in</strong>g along with it. Rice cultivation however is a major source of green house gasses, especially m<strong>et</strong>hane<br />

(CH4) (e.g. Sass 2005; Yan 2005). However, the alternation <strong>in</strong> w<strong>et</strong>t<strong>in</strong>g and dry<strong>in</strong>g to mitigate m<strong>et</strong>hane emissions<br />

can <strong>in</strong>crease nitrous oxide (N2O) emissions through enhanced nitrification and de-nitrification (Akiyama<br />

2005a & b). Complex mechanisms impact not only global warm<strong>in</strong>g potential (GWP) but also acidification<br />

(AP), eutrophication (EP) and photochemical ozone creation (POCP). The objective of this study was to<br />

assess the environmental performance of different rice cultivation systems <strong>in</strong> various countries and climates.<br />

Eight cropp<strong>in</strong>g systems have been chosen for data collection on precipitation, soil type, irrigation system,<br />

fertilisation, field operations, and pesticide use: conventional, irrigated, lowland rice cultivation <strong>in</strong> Ch<strong>in</strong>a<br />

(CC); deepwater rice cropp<strong>in</strong>g system <strong>in</strong> India (DWI); irrigated, conventional, lowland rice cultivation <strong>in</strong><br />

India with rice straw <strong>in</strong>corporation (II) and with rice straw burn<strong>in</strong>g (IB); irrigated, conventional, lowland rice<br />

cultivation <strong>in</strong> the Philipp<strong>in</strong>es with two cropp<strong>in</strong>g cycles (IP2) and with three cropp<strong>in</strong>g cycles per year (IP3);<br />

irrigated, organic rice cropp<strong>in</strong>g system <strong>in</strong> Japan (OUJ) and a ra<strong>in</strong>-fed, conventional, upland rice cultivation<br />

system <strong>in</strong> Japan (UJ). Rice systems were compared on a hectare (ha yr-1) as well as a product (kg ha-1) basis.<br />

The life cycle assessment followed ISO 14040. The <strong>in</strong>ventory quantities fossil/renewable primary energy<br />

demand (PED) and water use (WU) were analysed. GWP, AP, EP and POCP were computed accord<strong>in</strong>g to<br />

the CML m<strong>et</strong>hod (Gu<strong>in</strong>ée 2002).<br />

Upland rice systems (UJ and to some degree OUJ) showed lowest impacts among the rice-cropp<strong>in</strong>g systems<br />

tested <strong>in</strong> WU, GWP, AP and POCP and one of the lowest <strong>in</strong> PED and EP. OJ performed well <strong>in</strong> PED, GWP,<br />

POCP, AP and WU. On the other hand, the highest environmental impacts was caused by the systems IP2<br />

and IP3, due to high <strong>in</strong>puts of fertiliser, diesel <strong>et</strong>c. along with low yields. The ma<strong>in</strong> emissions were released<br />

<strong>in</strong> the field by decomposition of nitrogen <strong>in</strong>to NH3, NO3- and carbon <strong>in</strong>to CH4. Fertiliser production and diesel<br />

combustion <strong>in</strong> tractors and diesel generators of irrigation pumps were identified as additional sources of<br />

emissions. A removal of straw for bio-energy or burn<strong>in</strong>g on the field reduces nitrogen (i.e., N2O, NOx, NO3 − )<br />

and carbon related emissions (CH4). At the same time potential accumulation rate of soil organic carbon<br />

decreases and consequently <strong>in</strong>crease PED and GWP due to the additional demand for m<strong>in</strong>eral fertiliser. The<br />

ma<strong>in</strong> challenges were identified as the water regime and organic <strong>in</strong>puts, as well as the type of soil, the climate,<br />

the field management and the production and <strong>in</strong>tensity of fertiliser use.<br />

References<br />

Akiyama, H., Yagi, K., Yan, X., 2005. Summary of N2O emissions from rice paddy fields: Summary of<br />

available data. Global Biogeochemical Cycle 19: 1005.<br />

FAO (2010). FAOSTAT database, <strong>Food</strong> and Agriculture Organization (FAO). Rome<br />

Gu<strong>in</strong>ée, J. B., 2002. Handbook on <strong>LCA</strong>: Operational Guide to the ISO Standards. N<strong>et</strong>herlands<br />

Watanabe, A., Kimura, M., 1999. Influence of chemical properties of soils on m<strong>et</strong>hane emission from rice<br />

paddies. Commum Soil Sci Plant Anal. 30: 2449-2463.<br />

Yan, X., Yagi, K., Akiyama, H., Akimoto, H., 2005. Statistical analysis of the major variables controll<strong>in</strong>g<br />

m<strong>et</strong>hane emission from rice fields. Global Change Biology 11 (7): 1131-1141.<br />

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