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DISCUSSION<br />

The effects of weed mats on the sediments and invertebrate fauna of sheltered bays<br />

and sandflats have been studied by both descriptive surveys and controlled<br />

experimental manipulations. The objectives and underlying assumptions behind these<br />

two methods are very different and consequently often produce contrasting results.<br />

Therefore, this discussion will be limited to comparisons with, and conclusions<br />

relative to, other controlled algal-manipulation experiments. This will avoid this<br />

discussion becoming a hybrid between two fundamentally different approaches and,<br />

therefore, minimise inaccuracies. A comparative survey of the ecological effects of<br />

naturally occurring macroalgal mats on Drum Sands is given in Chapter 5.<br />

This study aimed at specifically investigating the ecological effects of macroalgal<br />

mats on intertidal sandflats and whether mat formation had a potential role in P.<br />

elegans patch formation. These will be discussed separately.<br />

The ecological effects of weed mats on intertidal sandflats.<br />

The E. prolifera implanted within the weed plots in this study successfully established<br />

from the time of implantation until October, a period of 20 weeks. After an initial<br />

reduction the weed remained at a fairly constant biomass. Six weeks after<br />

implantation the weed caused marked changes in the macrobenthos, together with<br />

changes in all the measured sediment variables. While the numbers of P. elegans<br />

were significantly reduced, those of C. capitata, oligochaetes and gammarids<br />

increased under weed mats. Water, organic matter and silt/clay contents, medium phi<br />

and sorting coefficients significantly increased in the sediments under weed mats,<br />

these sediments also became significantly more reducing between 1-8cm depth. After<br />

20 weeks, during weed decay, the effects of the weed on the fauna were similar to<br />

those after 6 weeks resulting in a community numerically dominated by C. capitata,<br />

while the sediment variables were no longer significantly different from controls.<br />

Weed implantation experiments carried out previously have been conducted on more<br />

sheltered sandflats and the methods of weed attachment, wire hoops for example, have<br />

been less obtrusive (Reise, 1983a; Hull, 1987). These published studies, in contrast to<br />

this study, did not incorporate a control treatment to determine whether there were any<br />

102

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