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

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PARALLEL SESSION 3A: LAND USE CHANGE 8 th Int. Conference on <strong>LCA</strong> <strong>in</strong> the<br />

Parallel session 3a: Land Use Change<br />

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

Bioenergy production from perennial energy crops: a consequential<br />

<strong>LCA</strong> of 12 bioenergy cha<strong>in</strong>s <strong>in</strong>clud<strong>in</strong>g land use changes<br />

Lorie Hamel<strong>in</strong> 1* , Davide Ton<strong>in</strong>i 2 , Thomas Astrup 2 , Henrik Wenzel 1<br />

1<br />

Institute of Chemical Eng<strong>in</strong>eer<strong>in</strong>g, Biotechnology and Environmental technology (KBM), University of Southern Denmark, Campusvej<br />

55, 5230 Odense M., Denmark<br />

2<br />

Department of Environmental Eng<strong>in</strong>eer<strong>in</strong>g, Technical University of Denmark, Miljøvej, Build<strong>in</strong>g 113, 2800 Lyngby, Denmark.<br />

Correspond<strong>in</strong>g author. E-mail: loha@kbm.sdu.dk<br />

ABSTRACT<br />

In the endeavour of optimiz<strong>in</strong>g the susta<strong>in</strong>ability of bioenergy production <strong>in</strong> Denmark, this consequential life cycle assessment<br />

(<strong>LCA</strong>) evaluated the environmental impacts associated with the production of heat and electricity from one hectare of Danish arable<br />

land cultivated with three perennial crops: ryegrass, willow and Miscanthus. For each, four conversion pathways were assessed<br />

aga<strong>in</strong>st a fossil fuel reference: I) anaerobic co-digestion with manure, II) gasification, III) combustion <strong>in</strong> small-to-medium scale<br />

biomass comb<strong>in</strong>ed heat and power (CHP) plants and IV) co-fir<strong>in</strong>g <strong>in</strong> large scale coal-fired CHP plants. Soil carbon changes, direct<br />

and <strong>in</strong>direct land use changes as well as uncerta<strong>in</strong>ty analysis (sensitivity, MonteCarlo) were <strong>in</strong>cluded <strong>in</strong> the <strong>LCA</strong>. Results showed<br />

that global warm<strong>in</strong>g was the bottleneck impact, where only two scenarios, namely willow and Miscanthus co-fir<strong>in</strong>g, allowed for an<br />

improvement as compared to the reference (-82 and -45 t CO2-eq. ha -1 , respectively).<br />

Keywords: perennial crops, combustion, land use changes, gasification, anaerobic digestion<br />

1. Introduction<br />

The ambition of the energy policy <strong>in</strong> Denmark is to reach a 100% renewable energy system by 2050<br />

(Lund <strong>et</strong> al., 2011). Several studies have been conducted to design and optimize such a system, and these all<br />

highlight the <strong>in</strong>dispensability of a biomass potential of around 35%–50% of the overall energy consumption<br />

(Lund <strong>et</strong> al., 2011; Energ<strong>in</strong><strong>et</strong>.dk, 2010; Klimakommissionen, 2010). Though biomass is a renewable energy<br />

source, it is not unlimited <strong>in</strong> supply, and does <strong>in</strong>volve considerable environmental costs. One of the most<br />

critical costs of bioenergy relates to its <strong>in</strong>cidence on land use changes (LUC) (Search<strong>in</strong>ger <strong>et</strong> al., 2008; Edwards<br />

<strong>et</strong> al., 2010), i.e. the conversion of land from one use (e.g. forest, grassland or food/feed crop cultivation)<br />

to another use (e.g. energy crop cultivation). One way to m<strong>in</strong>imize these LUC impacts could be through<br />

favour<strong>in</strong>g the cultivation of perennial energy crops (e.g. perennial ryegrass, willow and Miscanthus) <strong>in</strong>stead<br />

of annual crops (e.g. maize, barley, wheat, sugar be<strong>et</strong>). In fact, it is acknowledged that perennial energy<br />

crops nowadays represent the most efficient and susta<strong>in</strong>able feedstock available for bioenergy production <strong>in</strong><br />

temperate regions (Bessou <strong>et</strong> al., 2011).<br />

The goal of this study is to assess the environmental impacts associated with the production of bioenergy<br />

(heat and electricity) from 1 hectare (ha) of Danish arable land cultivated with ryegrass, willow and<br />

Miscanthus, consider<strong>in</strong>g four different biomass-to-energy (BtE) conversion pathways: i) anaerobic codigestion<br />

with manure, ii) gasification, iii) combustion <strong>in</strong> small-to-medium scale biomass comb<strong>in</strong>ed heat and<br />

power (CHP) plants and iv) co-fir<strong>in</strong>g <strong>in</strong> large scale coal-fired CHP plants.<br />

2. M<strong>et</strong>hods<br />

2.1. Life cycle assessment model<br />

The environmental assessment presented <strong>in</strong> this study was performed us<strong>in</strong>g consequential life cycle assessment<br />

(<strong>LCA</strong>). The functional unit upon which all <strong>in</strong>put and output flows were expressed is 1 ha of agricultural<br />

land used to grow the selected energy crops. The geographical scope considered for the <strong>LCA</strong> was<br />

Denmark, i.e. the data <strong>in</strong>ventory for crops cultivation and BtE plants were specific for Danish conditions.<br />

Similarly, the legislative context of Denmark (e.g. fertilisation) was considered. The temporal scope considered<br />

was 20 years, i.e. all assessed systems were operated for a 20 years duration. The life cycle impact assessment<br />

was carried out accord<strong>in</strong>g to the Danish EDIP 2003 m<strong>et</strong>hod (Hauschild and Pott<strong>in</strong>g, 2005), to<br />

which one impact category, “Phosphorous as resource”, was added based on the Impact 2002+ m<strong>et</strong>hod (Jolli<strong>et</strong><br />

<strong>et</strong> al., 2003). Background <strong>LCA</strong> data were based on the Eco<strong>in</strong>vent v.2.2 database, and the assessment was<br />

facilitated with the <strong>LCA</strong> software SimaPro 7.3.3. Foreground <strong>LCA</strong> data essentially <strong>in</strong>cluded Danish-specific<br />

data for agricultural and energy conversion processes, and the impacts associated with capital goods (foreground<br />

data only) as well as those related to transportation of the residues (i.e. ash and digestate) have been<br />

excluded. The systems assessed considered three perennial crops (ryegrass, willow and Miscanthus) and four<br />

BtE conversion technologies (anaerobic co-digestion, gasification, combustion <strong>in</strong> small-to-medium scale<br />

239

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