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sediment sampling, together with redox potential measurements, were repeated. At<br />

the end of the experiment, only 6% of each plot had been sampled and the precise core<br />

positions had been noted so that nowhere was repeatedly sampled.<br />

The weed biomass was determined twice during the experiment, after 6 weeks<br />

(maintained density) and 20 weeks (during decay). This was done by inserting a<br />

6x6cm corer randomly positioned into each weed treatment plot. The weed lying on<br />

the top of the sediment surface was collected and preserved in 10% saline<br />

formaldehyde solution. The weed was later washed in water to remove any fauna or<br />

sand grains then dried at 80°C for 24 hours and weighed (Everett, 1991). At low tide,<br />

the sediment was consistently more than 90% covered by the algae until it started<br />

disappearing in early October. The net plots noticeably collected some sediment and<br />

the nets became partially covered. Since the sediment is mobile at Drum Sands, it is<br />

likely that this could have been natural sediment movement and not due to the<br />

presence of the plastic mesh. Very small amounts of unanchored weed were present<br />

within the net plots after two weeks which were almost certainly drift fragments<br />

which had been deposited by the receding tide. These remained only loosely attached<br />

to the plastic mesh rather than establishing themselves within the sediments.<br />

The 5th setiger widths of the P. elegans were measured directly using the same<br />

technique as in Chapter 3. Size measurements were carried out on the individuals<br />

from the weed treatment and the control plots only since there were no significant<br />

differences in their numbers between the weed treatment and net plots (see Results).<br />

Therefore, it was concluded that there were no artefacts associated with the plastic<br />

mesh and any differences in the size-frequency distributions between the weed<br />

treatments and the control plots were due to the weed alone. All individuals within<br />

these plots which were complete to at least their 10th setiger were measured.<br />

Data analyses - Only those species with a mean abundance of more than one<br />

individual per core for any one treatment were included for analyses. The data were<br />

checked for normality using the Anderson-Darling test and for homogeneity of<br />

variance using the Bartlett test. Data not meeting these criteria were transformed<br />

91

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