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Drivers of environmental innovation - Vinnova

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according to Hemmelskamp (Forthcoming), reflect the lively debate on<br />

<strong>environmental</strong> taxes at the time. The results seem to show that economic<br />

instruments have advantages in the case <strong>of</strong> <strong>environmental</strong> product <strong>innovation</strong>s,<br />

but that there are no general advantages <strong>of</strong> one type <strong>of</strong> instrument over another<br />

related to <strong>environmental</strong> process <strong>innovation</strong>s (Hemmelskamp, Forthcoming).<br />

A common criticism against <strong>environmental</strong> taxation is that countries, which<br />

unilaterally adopt such policy measures, lose competitiveness. Carraro and<br />

Galeotti have reviewed studies that provide additional critical remarks. On the<br />

grounds <strong>of</strong> efficiency, emission permits have been shown to improve on<br />

emission charges when the inter-temporal decisions <strong>of</strong> agents, particularly on<br />

<strong>innovation</strong>, cannot be neglected. Moreover, when more than one externality has<br />

to be accounted for, <strong>environmental</strong> taxation must be combined with other<br />

policy instruments to achieve the social optimum. Information asymmetries<br />

(such as in non-point source pollution problems) invite policy interventions that<br />

are far more complex than <strong>environmental</strong> taxation (Carraro and Galeotti, 1997).<br />

A tax and its related revenue can be directed to foster technological <strong>innovation</strong>,<br />

but Carraro and Galeotti point to some recent analysis that shows that<br />

<strong>environmental</strong> taxes or emission permits are likely to be sub-optimal<br />

instruments for achieving an adequate level <strong>of</strong> technological <strong>innovation</strong>.<br />

Studies have shown that, in a dynamic framework, taxes or permits can lead to<br />

the over investment in <strong>environmental</strong> <strong>innovation</strong> (Carraro and Galeotti, 1997).<br />

Charges<br />

Charges stimulate voluntary and individual adaptations in order to prevent or<br />

reduce <strong>environmental</strong> impacts. Quite simply, the bigger the cost advantage <strong>of</strong><br />

innovating as compared to paying the charges the greater the incentive to<br />

innovate. The political process <strong>of</strong> fixing the rate <strong>of</strong> the charges is, however,<br />

difficult. Finding the most effective level presupposes information on the<br />

marginal avoidance costs <strong>of</strong> all polluters, information that in real life does not<br />

exist. Rather trial-and-error methods are used, and this hampers efficiency<br />

(Hemmelskamp, 1997).<br />

Tradable permits<br />

The term tradable permits refers to deliberately created markets where actors<br />

buy and sell “rights” or permits for actual or potential pollution.<br />

There are two basic models on how to construct a system <strong>of</strong> tradable<br />

permits/reductions: the cap and trade model and the baseline and credit<br />

model.<br />

The cap and trade model defines a total ceiling <strong>of</strong> pollution from polluters<br />

included withn a system. The total amount <strong>of</strong> pollution in the pollution cap is<br />

divided between the polluters. The shares allocated to the polluters could be<br />

given out free <strong>of</strong> charge or be auctioned <strong>of</strong>f. At the end <strong>of</strong> the period that is to<br />

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