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Scenario results<br />

The high electricity consumption for primary aluminium production results in a strong influence of the<br />

electricity generation on the CO2 emissions, as shown by figure 6. Thanks to the almost complete absence of<br />

process CO2 emissions, the bipolar electrode cell benefits more from a low electricity emission factor than Hall-<br />

HJroult does. The difference between primary and secondary routes is much smaller in case of a low electricity<br />

emission factor.<br />

A shift from the current<br />

Hall-HJroult cell to the Bipolar<br />

cell, accompanied by a zero<br />

electricity emissions factor,<br />

would mean an eight-fold reduction<br />

within primary production.<br />

In the same circumstances,<br />

a shift to secondary production<br />

means a thirty-fold reduction of<br />

CO2 emissions.<br />

Reduction Potential of the Sector<br />

The intermediate factor two reduction<br />

goal is attainable for<br />

steel, even with unfavourable<br />

external conditions. The<br />

CO2/t<br />

8<br />

6<br />

4<br />

2<br />

0<br />

Aluminium production<br />

CO2 emissions<br />

hall_heroult bipolar secondary<br />

Production route<br />

0 t CO2/GJe<br />

0.1 t CO2/GJe<br />

MIDREX based production route nearly realises 50 % reduction relative to the standard BF150 route, with a<br />

high electricity emissions factor and low scrap addition; high scrap addition further lowers emissions, beneath<br />

the 50 % goal. A factor 2 reduction in aluminium production is only attainable with a low electricity emissions<br />

factor.<br />

On the long term, steel production can meet the factor 10 reduction goal, if external parameters are favourable.<br />

CO2 removal is essential to attain the factor 10 reduction without changing the ratio between primary and scrap<br />

based production routes. The electricity emission factor and the scrap addition rate may be helpful for further<br />

reduction of emissions, but their influence is mainly to change the relative order of the production routes. On<br />

the long term the required changes of the infrastructure to enable CO2 storage are very probably attainable,<br />

though a social acceptation of the storage in aquifers and empty natural gas fields may raise difficulties.<br />

Compared with steel, aluminium lags somewhat behind; within the primary production routes a factor 8 is attainable<br />

with a low electricity emissions factor. Further reductions of emissions require a shift to scrap based<br />

production. If this is not attainable, extra reductions in steel production may compensate the deficiency in aluminium.<br />

Besides external factors, internal factors are likely to influence the choice of a production route. Of the production<br />

routes with considerable reduction potentials, COREX and CCF based routes present a logical step for<br />

primary steel producers, while DRI based routes are entirely different from the current primary production<br />

structure. On the other hand, DRI based routes might be a logical step for the current scrap based producers.<br />

MIDREX, Circofer and CCF could be regarded as Asafe bets@ as they always result in emission reductions,<br />

regardless of external parameters, while COREX requires CO2 removal to realise reductions at all. The CCF<br />

route has the advantage of its low costs, even in the removal scenarios.

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