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            <gco:CharacterString>[A] The final report in Microsoft Word and Adobe PDF formats. Ffynnon Reference Number DCT-12-231336. [B] A full set of maps produced in JPEG format (to be provided if available) [C] A series of GIS layers on which the maps in the report are based in MapInfo format (to be provided). [D] A series of spreadsheets in Microsoft xlsx format detailing; catch, habitat data, length/frequency data &amp; poultaion estimates - River Dee Lamprey Surveys_2011_All catch.xlsx - River Dee Lamprey Surveys_2011_Habitat Data.xlsx - River Dee Lamprey Surveys_2011_Length Frequency.xlsx - River Dee Lamprey Surveys_2011_Population Estimates_Optimal.xlsx - River Dee Lamprey Surveys_2011_Population Estimates_Sub-Optimal.xlsx  [E] Species data provide in Recorder 6 import format (Microsoft xlsx) Recorder_Import_template_V32_APEM.xlsx  [F] A full set of site images produced in jpg format (to be provided).</gco:CharacterString>
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                    <gmx:Anchor xlink:href="http://data.europa.eu/eli/reg/2010/1089">Commission Regulation (EU) No 1089/2010 of 23 November 2010 implementing Directive 2007/2/EC of the European Parliament and of the Council as regards interoperability of spatial data sets and services</gmx:Anchor>
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            <gco:CharacterString>In 2011 monitoring is a continuation of data collected in 2004, which included the capture of historical records from 1985 onwards.  Electrofishing methodologies were used.  Following the LIFE protocol, where possible, surveys were carried out in both optimal and sub-optimal habitat at each site. Habitats were surveyed quantitatively using an enclosed area as a barrier to fish movement. Where possible a 1 m2 quadrat, enclosed with 2 mm fine mesh netting was positioned over the selected habitat at each survey site and then left to settle. At sub optimal sites a complete 1 m2 area of habitat was often not present. In this case several areas of sub optimal habitat were sampled within the 100 m stretch to represent a combined area of 1 m2. Under these circumstances a quadrat was not used to enclose the sample area. Electric fishing was undertaken within the quadrat in such a way as to draw individual lamprey out of the sediment rather than stunning and trapping them in the silt. The anode was energised in short bursts of 20 seconds followed by 5 second gaps. This was carried out over a two minute period. This procedure was classed as a single run, which in optimal habitats was subsequently repeated at least twice within the same quadrat (with a five minute gap between runs). In sub-optimal habitats a single run was carried out at each site.</gco:CharacterString>
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