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shown to consume up to 68% of a 0-group C. edule population (Pihl and Rosenberg, 1984). Reise (1985) suggested that once C. edule have managed to escape their predators in their first summer, they are capable of establishing dense populations lasting about 5 years, unless they are killed by the next severe winter. Chapter 3 has shown that the P. elegans population on Drum Sands did not produce benthic larvae nor reproduce asexually, but instead had a dispersal mode of reproduction with planktotrophic larvae. Consequently, this population was particularly susceptible to adult-juvenile interactions and therefore likely to be replaced by suspension-feeding bivalves. For example, Commito (1987) and Commito and Boncavage (1989) suggested that only those tube-building or deposit- feeding species which produce cocoons or benthic larvae that are too large for siphonal inhalation are relatively immune from adult-larval interactions with suspension-feeding bivalves. It is not possible to suggest why 1998 saw the start of the interaction between the two species at Drum Sands and the onset of P. elegans patch decline. It was possibly due to a high C. edule spat-fall, low adult bivalve densities (facilitating successful juvenile C. edule settlement) or the relative timing of bivalve and spionid larval settlement. Since there were low adult C. edule densities at this time it is possible that adult densities may have been regulating C. edule recruitment. Successful C. edule spat settlement has been recorded during summers following severe winters which decimated adult populations (Smidt, 1944; Reise, 1985) and Kristensen (1957) concluded that high adult C. edule densities may prevent a successful settlement of larvae. C. edule has been shown to ingest its own larvae, in addition to other bivalve species (Jensen, 1985; Andre and Rosenberg, 1991). The almost complete absence of adult C. edule in P. elegans patches could have therefore been responsible for the increased number of juvenile C. edule observed in patches compared to non-patches in this study. 233
This study had 3 main aims, these were: CHAPTER 9 GENERAL DISCUSSION • To determine the spatial distribution of P. elegans on Drum Sands; • To investigate the processes affecting P. elegans densities and the possible role of these processes in the formation and maintenance of small-scale patches; • To assess the ecological importance of the spatial distribution of P. elegans on Drum Sands. These 3 main aims have been successfully fulfilled by the surveys and controlled experiments performed on Drum Sands and are now discussed separately. The spatial distribution of P. elegans on Drum Sands, Firth of Forth, Scotland. Irrespective of the field of study, all marine ecologists are faced with the problem of establishing and quantifying patterns in nature since they are the building blocks of the models from which hypotheses are generated (Andrew and Mapstone, 1987). In the first part of the present study, the small-scale (metres) and meso-scale (tens of metres) spatial patterns of P. elegans were determined, followed by an investigation of the micro-scale (centimetres) spatial patterns. The small- and meso-scale patterns were considered in Chapter 2 and the micro-scale patterns in Chapter 7. In Chapter 2 the presence of areas of smooth, raised sediments observed on Drum Sands were confirmed by spatial surveys to be areas of significantly higher densities of P. elegans. These 'patches' were found to be approximately 1-1.5m 2 and were randomly distributed. The detection of these patches was crucial to all later studies described within this thesis since these studies depended upon the presence of significantly increased numbers of P. elegans within patches compared with non- patch sediments. 234
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This study had 3 main aims, these were:<br />
CHAPTER 9<br />
GENERAL DISCUSSION<br />
• To determine the spatial distribution of P. elegans on Drum Sands;<br />
• To investigate the processes affecting P. elegans densities and the possible role of<br />
these processes in the formation and maintenance of small-scale patches;<br />
• To assess the ecological importance of the spatial distribution of P. elegans on<br />
Drum Sands.<br />
These 3 main aims have been successfully fulfilled by the surveys and controlled<br />
experiments performed on Drum Sands and are now discussed separately.<br />
The spatial distribution of P. elegans on Drum Sands, Firth of Forth, Scotland.<br />
Irrespective of the field of study, all marine ecologists are faced with the problem of<br />
establishing and quantifying patterns in nature since they are the building blocks of the<br />
models from which hypotheses are generated (Andrew and Mapstone, 1987). In the<br />
first part of the present study, the small-scale (metres) and meso-scale (tens of metres)<br />
spatial patterns of P. elegans were determined, followed by an investigation of the<br />
micro-scale (centimetres) spatial patterns. The small- and meso-scale patterns were<br />
considered in Chapter 2 and the micro-scale patterns in Chapter 7.<br />
In Chapter 2 the presence of areas of smooth, raised sediments observed on Drum<br />
Sands were confirmed by spatial surveys to be areas of significantly higher densities<br />
of P. elegans. These 'patches' were found to be approximately 1-1.5m 2 and were<br />
randomly distributed. The detection of these patches was crucial to all later studies<br />
described within this thesis since these studies depended upon the presence of<br />
significantly increased numbers of P. elegans within patches compared with non-<br />
patch sediments.<br />
234