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esulting community at any stage of succession is likely to depend upon the timing of the initial disturbance (Zajac and Whitlatch, 1982a; 1982b). Drum Sands is an ideal location in which to explicitly test certain aspects of population and community responses to disturbances. For example, it has been shown that the study area within Drum Sands contains a mosaic of communities in different successional stages with some species, for example, P. elegans, exhibiting pronounced patchiness (see Chapter 2). P. elegans has the ability to affect the hydrodynamics of near-bed flow and therefore the potential to affect settlement. Furthermore, this species has been shown to have a wide repertoire of reproductive strategies which was investigated in Chapter 3. Therefore, this system allowed certain questions about initial colonisation to be addressed. These were: 1 - do tube-bed areas have different early successional dynamics from non tube-bed areas?. This will be examined by comparing the initial communities of P. elegans patches with those of non-patch areas after a small-scale disturbance; 2 - does the successional stage of a community affect the colonisation mode of early colonisers?. This will be addressed by assessing the dispersal mode of the most abundant species to recently disturbed sediments within P. elegans patches with those from disturbances within non-patch sediments; 3 - can sediment disturbance lead to P. elegans patch formation on Drum Sands?. 133

METHODS Experimental design - Eighty P. elegans patches were individually numbered from within the 250x400m study area (Chapter 1) so that patches could be selected randomly for experimentation. Six P. elegans patches (hereafter referred to as 'patch' plots) were randomly chosen and a 1m 2 area marked within each by a small cane at each corner. The patches themselves were approximately 1-1.5m 2 in area (Chapter 2). Similarly, 6 plots were chosen outside P. elegans patches (hereafter referred to as 'non-patch' plots) by random co-ordinates within the study area and a 1m 2 area marked in the same way as for patch plots. Six replicates were chosen as this was decided to be the most that could be logistically sampled with respect to the amount of work involved and this was a sufficient number to allow non-parametric statistical analyses to be carried out if necessary. None of these plots had macroalgal mat cover either at the time of sediment implantation or at the time of sampling. Sediment was obtained by inserting 12 corers, 10cm diameter, into the sand within the study area from non-patch sediments to a depth of 12cm. The sediment was kept in the corers and frozen at -20°C for 3 days, thawed for 1 day and then refrozen. Sediment defaunation by freezing at this temperature has been successfully achieved in many studies (e.g., Bonsdorff and Osterman, 1984; Savidge and Taghon, 1988; Bonsdorff, 1989; Frid, 1989; Thrush et al., 1992). This freeze-thawing was repeated 6 times for each core. After treatment, no animals were found alive (n=6) and all the invertebrate taxa killed by this process were so severely damaged that they could easily be distinguished from invertebrates alive at the time of subsequent sampling (except nematodes). Any P. elegans tubes protruding from the treated sediment surfaces were removed. The sediment cores were kept intact throughout the freeze- thawing process, maintaining the original sediment structure was thought to reduce erosion when later replaced in the sand. The 12 defaunated sediments were implanted on the 18th April 1997, ensuring that the tops were flush with the surrounding sediment surface. One defaunated sediment core was inserted into each of the 6 patch plots and 6 non-patch plots (see Figure 6.1). A 1m2 quadrat was located on the predefined 1m 2 areas (see above), divided into 100 sections (10x10cm) with string and the defaunated sediments inserted after the 134

METHODS<br />

Experimental design - Eighty P. elegans patches were individually numbered from<br />

within the 250x400m study area (Chapter 1) so that patches could be selected<br />

randomly for experimentation. Six P. elegans patches (hereafter referred to as 'patch'<br />

plots) were randomly chosen and a 1m 2 area marked within each by a small cane at<br />

each corner. The patches themselves were approximately 1-1.5m 2 in area (Chapter 2).<br />

Similarly, 6 plots were chosen outside P. elegans patches (hereafter referred to as<br />

'non-patch' plots) by random co-ordinates within the study area and a 1m 2 area<br />

marked in the same way as for patch plots. Six replicates were chosen as this was<br />

decided to be the most that could be logistically sampled with respect to the amount of<br />

work involved and this was a sufficient number to allow non-parametric statistical<br />

analyses to be carried out if necessary. None of these plots had macroalgal mat cover<br />

either at the time of sediment implantation or at the time of sampling.<br />

Sediment was obtained by inserting 12 corers, 10cm diameter, into the sand within the<br />

study area from non-patch sediments to a depth of 12cm. The sediment was kept in<br />

the corers and frozen at -20°C for 3 days, thawed for 1 day and then refrozen.<br />

Sediment defaunation by freezing at this temperature has been successfully achieved<br />

in many studies (e.g., Bonsdorff and Osterman, 1984; Savidge and Taghon, 1988;<br />

Bonsdorff, 1989; Frid, 1989; Thrush et al., 1992). This freeze-thawing was repeated 6<br />

times for each core. After treatment, no animals were found alive (n=6) and all the<br />

invertebrate taxa killed by this process were so severely damaged that they could<br />

easily be distinguished from invertebrates alive at the time of subsequent sampling<br />

(except nematodes). Any P. elegans tubes protruding from the treated sediment<br />

surfaces were removed. The sediment cores were kept intact throughout the freeze-<br />

thawing process, maintaining the original sediment structure was thought to reduce<br />

erosion when later replaced in the sand.<br />

The 12 defaunated sediments were implanted on the 18th April 1997, ensuring that the<br />

tops were flush with the surrounding sediment surface. One defaunated sediment core<br />

was inserted into each of the 6 patch plots and 6 non-patch plots (see Figure 6.1). A<br />

1m2 quadrat was located on the predefined 1m 2 areas (see above), divided into 100<br />

sections (10x10cm) with string and the defaunated sediments inserted after the<br />

134

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