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CHAPTER 4. MAJOR TRENDS IN CONFLICT AND<br />

COOPERATION<br />

Alistair Rieu-Clarke<br />

The aim of this chapter is to assess the range of legal and institutional mechanisms that exist in<br />

<strong>Europe</strong> to monitor, predict, and pre-empt transboundary water conflicts. Trends in cooperative<br />

mechanisms related to <strong>Europe</strong>an transboundary waters are identified using an analytical<br />

framework in order to assess the legal scope, substantive water rights and obligations,<br />

procedural rules and mechanisms, dispute resolution mechanisms, and institutional<br />

arrangements. This analytical framework recognises the fact that the existence of an agreement<br />

between countries over their transboundary waters is not in itself sufficient to ensure hydropolitical<br />

resilience. The chapter makes the assumption that in order for a legal framework for transboundary<br />

waters to be equitable and sustainable over the long-term, a set of key components must be present.<br />

This chapter assesses how these key components have been developed within the <strong>Europe</strong>an<br />

transboundary water context.<br />

4.1 LEGAL SCOPE: SURFACE WATER TO DRAINAGE BASINS<br />

The first section assesses how legal and institutional arrangements leading to cooperation over<br />

transboundary waters in <strong>Europe</strong> have dealt with geographic scope. It is necessary to ensure that<br />

international regimes regulate all countries’ activities that might have a significant adverse impact on<br />

the interests of other countries sharing the same waters in order to promote hydropolitical resilience<br />

between countries. Adopting a basin approach is largely recognised as the most appropriate method of<br />

achieving such security (Wescoat, 1992). The most pertinent issues to consider are the inclusion of both<br />

surface and groundwater, the coverage of confined groundwater, and the accommodation for relevant<br />

linkages between land and water.<br />

In line with the increasing number of uses of <strong>Europe</strong>’s water resources, transboundary agreements<br />

have generally broadened their geographic scope to include surface and groundwater, and in some<br />

circumstances, the entire drainage basin. The 1992 Helsinki Convention defined “transboundary<br />

waters” in Article 1 as, “any surface or groundwaters which mark, cross or are located on boundaries<br />

between two or more States; wherever transboundary waters flow directly into the sea.”<br />

The main purpose of the 1992 Helsinki Convention is to require contracting parties to take all<br />

appropriate measures to prevent, control, and reduce any transboundary impact. Pursuant to the<br />

convention, “transboundary impact” is defined as “any significant adverse effect on the environment<br />

resulting from a change in the conditions of transboundary waters caused by a human activity, the<br />

physical origin of which is situated wholly or in part within an area under the jurisdiction of a Party,<br />

within an area under the jurisdiction of another Party.” The way in which ‘transboundary impact’ is<br />

defined under the 1992 Helsinki Convention implies a wide geographic scope; not only does the<br />

convention cover transboundary surface water and groundwater but it also covers land-based activity<br />

affecting the conditions of transboundary waters. Therefore, the convention would cover pollution from<br />

agricultural practices, such as the use of pesticides and fertilisers that filter through the soil and into<br />

Chapter 4. Major Trends in Conflict and Cooperation — 43

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