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              <gmd:extent>
                <gml:TimePeriod gml:id="248c7e00-d37b-4ddd-b574-dacec9ced31b">
                  <gml:beginPosition>1988-04-11</gml:beginPosition>
                  <gml:endPosition>1988-05-04</gml:endPosition>
                </gml:TimePeriod>
              </gmd:extent>
            </gmd:EX_TemporalExtent>
          </gmd:temporalElement>
        </gmd:EX_Extent>
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        <gmd:MD_Format>
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                    <gmx:Anchor xlink:type="simple" 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:Date>2010-12-08</gco:Date>
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            <gco:CharacterString>Sampling: Plankton samples were taken with a modified version of the Lowestoft 
76 cm diameter high-speed sampler. This was modified by increasing the overall 
length from 2.13 m to 2.75 m and by fitting a conical nose cone with an 
aperture of 40 cm diameter instead of a hemispherical one. The sampler was 
fitted with a 270 µm aperture mesh resulting in an open area to nose cone 
aperture ratio of 12:1. The sampler was deployed at a nominal speed of 2.5 m s
-¹ in a double oblique tow from the surface to within 2 m of the seabed. 
Veering and hauling speeds were manually adjusted to ensure that each depth 
band was sampled equally. On recovery, the net was carefully washed down and 
the sample collected from the end bag. Each sample was then fixed in a 4% 
(w/v) formaldehyde solution and returned to the laboratory for analysis. The 
sampler, towed on a multi-cored electric cable, was fitted with both internal 
and external electronic flowmeters. Output was logged directly using a deck 
unit and used to calculate the volume of water filtered on each deployment. 
The flowmeters were calibrated in situ on the sampler using a circulating 
water channel. Under normal operating conditions, the sampler body accepts 
over ninety per cent of the theoretical volume of water offered to it at 2.5 m 
s-¹. Even under severe clogging, fifty per cent of this volume would still 
be filtered.

The plankton sampler was fitted with a Guildline CTD sensor package and 
recording system which was used to continuously monitor temperature and 
salinity throughout the deployment. CTD systems were routinely calibrated at 
the beginning and end of each survey. The levels of precision (as the standard 
deviation about the mean based on the manufacturer's calibrations) were ± 0.04 
psu for salinity and**±**0.02 ̊C for temperature.

Plankton sample sorting and sub-sampling: Initially the 1982 and 1985 samples 
were sorted only for the larvae of *Nephrops norvegicus*. The samples were 
subsequently analysed for fish eggs and larvae, with the exception of the 
third survey in 1985 from 19-26 May, which had an incomplete coverage of the 
area. The samples taken in 1987,1988 and 1989 were sorted for all species. 
Fish eggs and larvae were picked out from all samples by eye and, whenever 
practicable, the whole sample was sorted. However sub-sampling was at times 
necessary. Aliquots were removed using a 20 or 30 ml measured scoop. Fish 
larvae were readily identified unless they had been badly damaged during 
collection or were prematurely hatched. For some groups such as the sandeels 
(Ammodytidae) and the group of Gadidae commonly called rocklings, individuals 
were not identified to the species level. Fish eggs were initially split into 
three groups on the basis of the presence or absence of oil globules. Those 
containing either a single or many oil globules could usually be identified to 
the species level. Eggs with no oil globules were more difficult to identify. 
Some of these species such as cod (*Gadus morhua*), sprat (*Sprattus 
sprattus*), long rough dab (*Hippoglossoides platessoides*), dragonet
*(Callionymus* spp.) and plaice (*Pleuronectes platessa*) were identified 
because of their unique size or special features. Unidentified eggs in this 
group were recorded as egg diameters.

Data analysis and data storage (original):The raw data were stored in a 
customised database, initially using INGRES version 5, then transferred at a 
later date to Access version 2. The various data files were stored on the 
database in a series of tables linked by having the content of certain fields 
in common. All routine calculations, calibration changes and conversions were 
carried out on the database. The data has now been extracted into comma 
separated variable files.

Plankton data are normally expressed as either number of organisms per m3 or 
per m2. The number per m3 is obtained by dividing the numbers per sample by 
the volume filtered, calculated from the sampler flowmeters. Number per m2 is 
obtained by multiplying the number per m3 by the mean sampled depth during a 
deployment.</gco:CharacterString>
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