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emoved since they were the only taxa which colonised in sufficient numbers for size-<br />

frequency determination (see later). Very few young stages of the other<br />

macroinvertebrate species could be observed passing through this sieve. The 3-12cm<br />

fractions of the samples were sieved on a 500).tm mesh sieve before preserving. These<br />

samples, from the treated sediments, are hereafter referred to as `azoic' samples.<br />

One sample (control core, Figure 6.1) from each plot was also taken at the same time<br />

as the azoic sample. The results from these samples will not be presented here. They<br />

will be referred to, however, where necessary to give background information on<br />

faunal densities in ambient sediments. The results from these samples form part of<br />

Chapter 8 which focuses upon the faunal and sediment differences between patches<br />

and non-patches. Sampling methods, sample treatment, faunal sorting and<br />

identification and statistical analyses for Chapter 8 were carried out in an identical<br />

manner to those described here.<br />

The experiment was repeated on the 18th August and the 18th December 1997 using<br />

different P. elegans patch and non-patch plots in each experiment. The timings of the<br />

3 experiments were aimed to coincide with high P. elegans larval availability (April),<br />

moderate larval availability (August) and low availability (December)(see Chapter 3).<br />

This was later confirmed by the abundances of P. elegans juveniles in Figure 6.2(ii).<br />

The P. elegans individuals were divided into two groups a posteriori based on size.<br />

Size measurements were carried out in an identical way to Chapter 3. The smallest<br />

group ( 0.27mm, 5th setiger width) were considered to be 'juveniles' and those above<br />

this size were considered to be 'adults'. These size definitions were determined from<br />

the size distribution histograms (see results) - juveniles are those individuals which,<br />

based on the size-frequency histograms, had settled from the plankton within the 3<br />

week experimental period. All juvenile individuals sampled had already begun tube<br />

construction at the time of sampling and, therefore, could be classed as settled larvae<br />

as opposed to transients.<br />

To determine whether there were any differences in the environmental variables of the<br />

disturbed sediments between the two plot types, an additional experiment was carried<br />

137

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