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Section 06 - UKOTCF

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limits on production (h) and simplifies the environment<br />

by favouring a narrow range of productive<br />

types (i). This increases production (h), but causes<br />

widespread pollution, soil erosion and loss of<br />

biodiversity. It also displaces inherited diversity (j)<br />

in the form of locally adapted types and involves<br />

the convergent selection (k) of a narrow range of<br />

productive types dependent on the external inputs<br />

provided. This further simplifies the environment<br />

and compromises the provision of natural capital<br />

and ecosystem services (l).<br />

The processes illustrated by Figure 3 support the<br />

‘linkage’ model (O’Neill et al. 1998). They also<br />

provide policymakers with a conceptual tool for<br />

identifying ways of building restraints into economic<br />

policies by decreasing external inputs (g),<br />

protecting biodiversity (c, d, e) and integrating the<br />

value of natural capital and ecosystem services into<br />

economic processes (sensu Hindmarch et al. 20<strong>06</strong>),<br />

rather than counting them as ‘free goods’ (see<br />

Definitions).<br />

Emergence of sustainable development initiatives<br />

at a European level<br />

The adverse environmental impacts of the CAP<br />

experience provided a compelling argument for a<br />

rapid realignment of farming subsidies. However,<br />

there were also concerns that farm subsidies were<br />

becoming too expensive and would increase with<br />

the planned accession of the Central European<br />

States (Schröder 2002). It was also becoming apparent<br />

that these subsidies were beginning to complicate<br />

world trade negotiations (Europa 2004).<br />

These influences combined to favour an approach<br />

to policy development that increasingly addresses<br />

causes rather than symptoms (Figure 4). This has<br />

helped to put the concerns of biodiversity and sustainable<br />

development at the heart of European affairs<br />

through a succession of initiatives, including<br />

the European Union Biodiversity Strategy (EUBS<br />

1998), its related Action Plans (EUBAP 2001) and<br />

the ongoing Malahide process (EC 20<strong>06</strong>). Importantly,<br />

it has also informed the development and<br />

review of the European Sustainable Development<br />

Strategy (EUSDS 20<strong>06</strong>), which now includes provisions<br />

that will:<br />

• Eliminate policies that are ‘incompatible with<br />

sustainable development’ (EUSDS 20<strong>06</strong>, para.<br />

24);<br />

• Improve the ‘management and avoid overexploitation<br />

of natural<br />

resource’<br />

(EUSDS 20<strong>06</strong>,<br />

para. 13);<br />

• Encourage<br />

‘recognizing<br />

the value<br />

of ecosystem<br />

services’<br />

(EUSDS,<br />

20<strong>06</strong>, para.<br />

13).<br />

Figure 4. Development of European environmental policy: schematic representation. Adapted<br />

from Hindmarch et al. (20<strong>06</strong>).<br />

These paradigm-shifting<br />

provisions are<br />

part of a highlevel<br />

fiscal<br />

and regulatory<br />

framework<br />

for sustainable<br />

economic<br />

growth. Over<br />

time, this<br />

could help to<br />

protect the environment<br />

and<br />

its biodiversity<br />

Making the Right Connections: a conference on conservation in UK Overseas Territories, Crown Dependencies and other small island communities, page 190

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