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Common Implementation Strategy for the Water Framework Directive

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WFD CIS Guidance Document No.9<br />

Implementing <strong>the</strong> Geographical In<strong>for</strong>mation Systems (GIS) of <strong>the</strong> <strong>Water</strong> <strong>Framework</strong> <strong>Directive</strong><br />

automatically <strong>for</strong>ming unique European identification codes. Examples are provided here in<br />

order to clarify this point.<br />

There may be a number of authorities, such as counties, regions or Länders, responsible <strong>for</strong><br />

<strong>the</strong> establishment of monitoring stations. Each may have sub-authorities such as urban district<br />

councils with similar responsibilities. In such a case, it is useful if coding authorities are first<br />

assigned unique identifiers at Member State level. For example <strong>the</strong> initial two digits of a four<br />

digit authority code ‘AAAA’ might be used, e.g., ‘4000’, ‘1700’ or ‘2300’. The last two digits<br />

might be used to identify sub-authorities or regional offices. For example ‘1710’, ‘1714’, etc.<br />

These authorities can <strong>the</strong>n easily generate locally unique codes. A local code becomes<br />

nationally unique by <strong>the</strong> addition of <strong>the</strong> AAAA code as a header, and internationally unique<br />

by <strong>the</strong> fur<strong>the</strong>r addition of <strong>the</strong> MS code. For example, if a monitoring station is locally given<br />

<strong>the</strong> unique identifier of ‘12345’ by coding authority 1700 in Denmark, <strong>the</strong>n that station would<br />

be uniquely identified as DK170012345 when reporting to Europe.<br />

This approach is strongly recommended where multiple agencies are, or will be, involved in<br />

<strong>the</strong> ongoing identification of features. Exact coding structures to be used will be a matter <strong>for</strong><br />

individual Member States to decide upon and <strong>the</strong>se are likely to vary by feature type.<br />

3.4.3.2 Unique Identification Coding at Operational Levels<br />

The above technique can be taken fur<strong>the</strong>r within coding authorities, where appropriate. For<br />

example, if drinking water abstraction monitoring is managed at drinking water scheme level,<br />

<strong>the</strong>n a coding authority may first assign unique identifiers to drinking water schemes. The<br />

scheme managers can <strong>the</strong>n easily assign unique identifiers to monitoring stations at a local<br />

level.<br />

3.4.3.3 Using <strong>the</strong> River Network <strong>for</strong> Unique Code Assignments<br />

Once <strong>the</strong> river network has been uniquely coded, it can be used to assign unique codes to<br />

features that are connected to it. This provides ano<strong>the</strong>r mechanism <strong>for</strong> assignment of unique<br />

codes at a local level without having to cross check against national assignments.<br />

River segment identification codes can be used locally to assign unique codes to:<br />

�� river water bodies;<br />

�� lakes;<br />

�� lake water bodies;<br />

�� transitional water bodies; and<br />

�� <strong>the</strong> monitoring stations <strong>for</strong> all of <strong>the</strong>se.<br />

As explained later, <strong>the</strong> outlet river segment code should generally be used <strong>for</strong> hydrologically<br />

connected features that are associated with multiple river segments.<br />

For example, monitoring stations can be identified with codes that are an extension of river<br />

codes. The first two digits of a 4-digit monitoring station code ‘MMMM’ might be used. The<br />

last two digits could be used at a later stage to allow fur<strong>the</strong>r stations to be inserted, while<br />

maintaining a sequence to <strong>the</strong> order of stations. Such a sequence would be important <strong>for</strong> <strong>the</strong><br />

purpose of visual confirmation of uniqueness.<br />

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