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Assessing Temporary Carbon Storage in Life Cycle Assessment and ...

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One argument for this methodological choice of a 100-year cut-off is the assumption that <strong>in</strong> the future<br />

humanity will be better positioned to cope with climate change through e.g. technological<br />

improvements (see Sections 3.5 <strong>and</strong> 3.6 <strong>and</strong> [5] ).<br />

1.3 Tonne-year approaches<br />

The first presentation, given by the organisers of the workshop, <strong>in</strong>troduced the problematic of<br />

temporary carbon storage, <strong>and</strong> presented the aim of the workshop, which was to review available<br />

options <strong>and</strong> to discuss the most appropriate method for account<strong>in</strong>g for the potential benefits of<br />

temporary carbon storage <strong>in</strong> LCA <strong>and</strong> CF. The Moura-Costa [6] <strong>and</strong> the Lashof [7] methods, both<br />

tonne-year approaches developed for that purpose <strong>and</strong> presented <strong>in</strong> the IPCC special report on l<strong>and</strong><br />

use, l<strong>and</strong>-use change <strong>and</strong> forestry (LULUCF) [8], were presented.<br />

The Moura-Costa <strong>and</strong> the Lashof approaches were proposed ten years ago to account for temporary<br />

carbon storage. Some participants expla<strong>in</strong>ed that these authors were <strong>in</strong>volved <strong>in</strong> the development of<br />

the IPCC special report on LULUCF published <strong>in</strong> 2000 [8], <strong>and</strong> that the subject was closed <strong>in</strong> 2003,<br />

when the IPCC published the good practice guidel<strong>in</strong>es adopt<strong>in</strong>g the mass balance stock change<br />

approach. Some years after that, tim<strong>in</strong>g issues were aga<strong>in</strong> receiv<strong>in</strong>g attention with the development of<br />

the British st<strong>and</strong>ard PAS 2050 for carbon footpr<strong>in</strong>t<strong>in</strong>g, where benefits are given to temporary carbon<br />

storage <strong>and</strong> delayed emissions. Other st<strong>and</strong>ards still <strong>in</strong> development, such as the GHG Protocol <strong>and</strong><br />

ISO14067, are also <strong>in</strong>vestigat<strong>in</strong>g temporal issues.<br />

These tonne-year methods aim at calculat<strong>in</strong>g a credit <strong>in</strong> kg-eq CO 2 for keep<strong>in</strong>g carbon out of the<br />

atmosphere for a given number of years. This credit can then be subtracted from a GHG <strong>in</strong>ventory, as<br />

it is assumed to compensate for the impact of an equivalent GHG emission.<br />

The basel<strong>in</strong>e for these methods is the cumulative radiative forc<strong>in</strong>g, <strong>in</strong>tegrated over a given time<br />

horizon (usually 100 years), caused by a one-tonne pulse-emission of CO 2 . For a time horizon of 100<br />

years, the <strong>in</strong>tegral of the CO 2 decay curve is approximately 48 tonne-years.<br />

The Moura-Costa approach (see Figure 1) is based on a fixed duration over which impacts occur after<br />

an emission. This reflects typical practice <strong>in</strong> LCA <strong>and</strong> CF, as the time when an emission occurs is not<br />

considered. Accord<strong>in</strong>g to this approach, 48 tonne-years of CO 2 is equivalent to 1 tonne of CO 2 -eq.<br />

Consequently, stor<strong>in</strong>g one tonne of CO 2 for 48 years is equivalent to avoid<strong>in</strong>g the impact of a onetonne<br />

CO 2 emission, which also means that stor<strong>in</strong>g one tonne of CO 2 for one year can fully<br />

compensate for the impact of an emission of 0.02 tonne (1/48) of CO 2 .<br />

Alternatively, the Lashof approach (see Figure 2) considers that stor<strong>in</strong>g carbon for a given number of<br />

years is equivalent to delay<strong>in</strong>g a CO 2 emission until the end of the storage period. The decay curve is<br />

3

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