12.03.2015 Views

Thesis-Anne-Vos-Masters-SBR-and-EU-Law-3

Thesis-Anne-Vos-Masters-SBR-and-EU-Law-3

Thesis-Anne-Vos-Masters-SBR-and-EU-Law-3

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

3.4 Water Framework Directive<br />

On 23 October 2000, the Directive (2000/60/EC) of the European Parliament <strong>and</strong> of the Council<br />

establishing a framework for the Community action in the field of water policy - in short: the Water<br />

Framework Directive (WFD) - was adopted. The WFD has integrated several water directives. The<br />

WFD contains an integrated river basin approach. It aims at establishing an integral approach with<br />

other policies <strong>and</strong> (water) directives. This is especially visible with the integral river basin<br />

management plan. 107 The objectives of the WFD are very broad, whereby other policies can be<br />

included. The quality of surface water <strong>and</strong> groundwater receive special attention. Therefore, two<br />

separate directives are adopted: the Groundwater Directive (2006/118/EC), which has been<br />

developed in response to the requirements of Article 17 WFD, <strong>and</strong> the Surface Water Directive<br />

(2008/105/EC). There is also a separate framework directive for the Marine Strategy (2008/56/EC),<br />

but this directive is not of much relevance for shale gas activities.<br />

Relevance for shale gas activities<br />

There is much debate on this Directive <strong>and</strong> the application thereof on shale gas activities,<br />

especially with regard to Article 11(3)(j). 108 Article 11 concerns the establishment of a programme<br />

of measures which every MS shall ensure for each river basin district. Each programme of<br />

measures shall include the basic measures, which are the minimum requirements to be complied<br />

with <strong>and</strong> which shall consist of inter alia Article 11(3)(j): a prohibition of direct discharges of<br />

pollutants (any substance liable to cause pollution) into groundwater subject to the provisions<br />

provided therein. MS may authorise reinjection into the same aquifer of water used for geothermal<br />

purposes. They may also authorise, specifying the conditions for inter alia:<br />

injection of water containing substances resulting from the operations for exploration <strong>and</strong> extraction<br />

of hydrocarbons or mining activities, <strong>and</strong> injection of water for technical reasons, into geological<br />

formations from which hydrocarbons or other substances have been extracted or into geological<br />

formations which for natural reasons are permanently unsuitable for other purposes, (…) provided<br />

such discharges do not compromise the achievement of the environmental objectives established for<br />

that body of groundwater.<br />

According to the Legal Assessment, conducted by the European Commission in 2011, Article<br />

11(3)(j) does not apply to shale gas activities since it does not allow flow-back water to be injected<br />

into geological formations. 109 Therefore, the Commission argues, the Mining Waste Directive<br />

applies here. In a latter working document of the Commission (of January 2014), it seems that the<br />

Commission finds the WFD applicable after all. Here, the Commission states that the identification<br />

of whether shale gas activities are a direct discharge of pollutant into groundwater would require a<br />

'site-specific hydrogeological risk assessment', for which no criteria are made available within the<br />

WFD. Therefore, this assessment depends on the discretion of the MS. This could lead to adverse<br />

consequences for groundwater, which would compromise the achievement of the environmental<br />

objectives established in the WFD. Moreover, there is discussion on the difference between direct<br />

<strong>and</strong> indirect discharge of pollutants into the groundwater with regard to hydraulic fracturing. The<br />

Commission gives as an example for this confusion: "whether a possible groundwater<br />

contamination following an unexpected extension of the fractures beyond the shale formation<br />

would qualify as direct or indirect discharge of pollutants." 110 Another point referred to by the<br />

Commission is that the WFD, concerning the waters used for the abstraction of drinking water, only<br />

requires MS to identify the bodies of water used for this abstraction within each river basin<br />

district. 111 Hence, monitoring at the level of the project site is not necessary. This would make it<br />

107<br />

Havekes & Van Rijswick (2012), pp. 101-107.<br />

108<br />

Commission Staff Working Document Impact Assessment (2014), part 4/4, p. 32.<br />

109<br />

Legal Assessment (2012), p. 7.<br />

110<br />

Commission Staff Working Document Impact Assessment (2014), part 4/4, p. 32.<br />

111<br />

Article 7 WFD.<br />

25

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!