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Comparative analysis of Maritime Spatial Planning ... - Seanergy 2020

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Before going any further in terms <strong>of</strong> assessing the extent to which existing legal and policy frameworks giveeffect to MSP it is perhaps useful to examine in more detail what is meant by MSP. An immediate problemin this respect is that there is no internationally accepted definition <strong>of</strong> MSP. Nor, <strong>of</strong> course, is there aformal EU definition given that there is no EU legislation on MSP.One broadly accepted definition, which has been proposed by UNESCO Intergovernmental OceanographicCommission (IOC) is that MSP is: ‘a process <strong>of</strong> analysing and allocating parts <strong>of</strong> three-dimensional marinespaces to specific uses to achieve ecological, economic and social objectives that are usually specifiedthrough the political process: the … process usually results in a comprehensive plan or vision for a marineregion. (MSP) is an essential element <strong>of</strong> sea use management’ (Ehler & Douvere, 2007).Although none <strong>of</strong> the EU‟s formal Communications on MSP to date have sought to define the concept, abrochure that has recently been produced by the European Commission (European Commission, 2010)contains the following definition:MSP is a process for planning and regulating all human uses <strong>of</strong> the sea, which also sets out toprotect the marine ecosystems in which these activities take place and safeguard marinebiodiversity. MSP is a process for planning and regulating all human uses <strong>of</strong> the sea, which alsosets out to protect the marine ecosystems in which these activities take place and safeguardmarine biodiversity.Of course while this too is not legally binding, two clear messages emerge from both <strong>of</strong> the definitions,namely: (a) that MSP is a process; and (b) moreover one that takes a comprehensive approach to humanactivities at sea.The adoption <strong>of</strong> policy statements and legislation in support <strong>of</strong> the development <strong>of</strong> the O-RE sector clearlyrepresents an important step forward in the development <strong>of</strong> a robust legal and policy framework for thesector. Examples <strong>of</strong> such legislation include the Spanish Royal Decree (RD) 1028/2007, a series <strong>of</strong>Belgian Royal Decrees 4 including the Decree <strong>of</strong> 3 February 2011. However such instruments cannot, in4 Royal decree <strong>of</strong> 7 September 2003 concerning the procedure for licences and the authorization <strong>of</strong> certain activitiesin the marine areas under Belgian jurisdiction (License Decree), Royal decree <strong>of</strong> 9 September 2003 concerning therules <strong>of</strong> an environmental impact assessment (Environmental Impact Decree), Royal Decree <strong>of</strong> 16 July 2002concerning the mechanisms to promote electricity production from renewable energies sources, Royal Decree <strong>of</strong> 20December 2000 giving the conditions for granting a domain concession and modified by the Royal Decree <strong>of</strong> 17 May2004 (MB26/06/2004), as well amended by the Royal Decree <strong>of</strong> 3 February 2011, Royal Decree 28 September 2008on the location <strong>of</strong> wind plants as a sine qua non condition to obtain a domain concessionDeliverable 2.38 | P a g e

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