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B<strong>and</strong>, <strong>and</strong><br />

approximate<br />

distance in miles<br />

from<br />

Table 4.2.6: UK air passenger duty as of November 1, 2009<br />

In the lowest class of travel (reduced<br />

rate)<br />

From November 1,<br />

2009 to October<br />

31, 2010<br />

From November 1,<br />

2010<br />

In other than the lowest class of travel *<br />

(St<strong>and</strong>ard rate)<br />

From November 1,<br />

2009 to October<br />

31, 2010<br />

From November 1,<br />

2010<br />

B<strong>and</strong> A (0-2,000) £11 £12 £22 £24<br />

B<strong>and</strong> B (2,001-<br />

4,000) £45 £60 £90 £120<br />

B<strong>and</strong> C (4,001-<br />

£50 £75 £100 £150<br />

6,000)<br />

B<strong>and</strong> D (over 6,000) £55 £85 £110 £170<br />

*<br />

The reduced rates apply where the passengers are carried in the lowest class of travel on any flight unless the seat<br />

pitch exceeds 1.016 metres (40 inches), in which case, whether there is one or more than one class of travel the<br />

st<strong>and</strong>ard rates apply.<br />

(Source: HM Revenue & Customs, 2008)<br />

Scientifically, there is general consensus that a “serious” climate policy approach will be paramount in the<br />

transformation of tourism towards becoming climatically sustainable, as significant technological<br />

innovation <strong>and</strong> behavioural change will dem<strong>and</strong> strong regulatory environments (e.g. Barr et al., 2010;<br />

Bows et al., 2009; Hickman <strong>and</strong> Banister, 2007; see also Giddens, 2009). As outlined by Scott et al. (2010),<br />

“serious” would include the endorsement of national <strong>and</strong> international mitigation policies by tourism<br />

stakeholders, a global closed emission trading scheme for aviation <strong>and</strong> shipping, the introduction of<br />

significant <strong>and</strong> constantly rising carbon taxes on fossil fuels, incentives for low-carbon technologies <strong>and</strong><br />

transport infrastructure, <strong>and</strong>, ultimately, the development of a vision for a fundamentally different global<br />

tourism economy.<br />

While this would dem<strong>and</strong> a rather radical change from current business models in tourism, all of these<br />

aspects of a low-carbon tourism system are principally embraced by business organisations. For instance,<br />

the World Economic Forum (WEF, 2009) suggests as mechanisms to achieve emission reductions i) a carbon<br />

tax on non-renewable fuels, ii) economic incentives for low-carbon technologies, iii) a cap-<strong>and</strong>-trade system<br />

for developing <strong>and</strong> developed countries, <strong>and</strong> iv) the further development of carbon trading markets.<br />

Furthermore, evidence from countries seeking to implement low-carbon policies suggests that the tourism<br />

businesses themselves also call for the implementation of legislation to curb emissions, a result of the wish<br />

for “rules for all”, with pro-climate oriented businesses dem<strong>and</strong>ing regulation <strong>and</strong> the introduction of<br />

market-based instruments to reduce emissions (cf. Ernst & Young, 2010; PricewaterhouseCoopers, 2010).<br />

There is consequently growing consensus among business leaders <strong>and</strong> policy makers that emissions of<br />

greenhouse gases represent a market failure. The absence of a price on pollution encourages pollution,<br />

prevents innovation, <strong>and</strong> creates a market situation where there is little incentive to innovate (OECD,<br />

2010). While governments have a wide range of environmental policy tools at their disposal to address this<br />

problem, including regulatory instruments, market-based instruments, agreements, subsidies, or<br />

information campaigns, the fairest <strong>and</strong> most efficient way of reducing emissions is increasingly seen in<br />

higher fuel prices, i.e. the introduction of a tax on fuel or emissions (e.g. Sterner, 2007; Mayor <strong>and</strong> Tol,<br />

2007, 2008, 2009, 2010a,b; see also OECD, 2009 <strong>and</strong> 2010; WEF, 2009; PricewaterhouseCoopers, 2010).<br />

Compared to other environmental instruments, such as regulations concerning emission intensities<br />

or technology prescriptions, environmentally related taxation encourages both the lowest cost<br />

abatement across polluters <strong>and</strong> provides incentives for abatement at each unit of pollution. These<br />

52

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