Fróðskaparrit - 31.12.2000, Side 112

Fróðskaparrit - 31.12.2000, Side 112
116 DOMINANT SPECIES ABUNDANCE RELATED TO ENVIRONMENTAL FACTORS ON ROCKY SHORES IN THE FAROE ISLANDS the ordination diagram, thus failing to de- monstrate any large negative effect of Litto- rina on any of the included species living at the same station, but not necessarily at the same level. The apparent large effect of Lit- torina was therefore probably not due to a negative effect of grazing, but rather to it often occuiTÍng together with certain speci- es. However, grazing may be a secondary explanation for this coexistence, as L. obtu- sata is known to use Ascophyllum nodosum as the main food source (Watson and Nor- ton, 1987), probably without having a sig- nificant negative effect on the population level of the host. It is also probable that juvenile L. obtusata use microalgae on the algal surface as a food source (Williams, 1990), thus reducing the epiphytic growth on the host plant. Such interactions might possibly explain some of the variation extracted by the first axis in the partial CA, and consequently also along the first DCA axis. As seen by the low amount of variance explained, grazing by Patella was not shown to have any large effect. Semibal- anus and Mytilus, which are predated on by Nucella, had their centroids near the zero value of the Nucella vector, thus failing to demonstrate any predation effect. When interpreting these results, two points should be kept in rnind. First, the scaling: Significant effects of grazing and predation might have been detected more locally than on 8 m stretches of shoreline. Second, the sampling method, by which only the abundance of a species was record- ed for the horizontal zone where it was most abundant: Recording of total abun- dance might have been more sensitive to grazing and predation effects. The results suggest, however, that on an intermediate scale the maximal abundances of the inves- tigated species were not strongly affected by grazing by Littorina or Patella or preda- tion by Nucella, except possibly indirectly by Littorina grazing. Species abundance curves Considering the earlier discussion, the species abundance curves along the first DCA axis may be assumed to represent the species responses to the main environmen- tal factor(s). All species abundance curves, except those for Mytilus edulis, Palmaria palmata and Patella vulgata, were signifi- cant at a 5% level, but the test is only sug- gestive, as the ordinal abundance data hard- ly fit a Gaussian distribution pattern. As Fig. 4 shows, the species may be divided into three main groups. The first group in- creased in abundance with increasing site scores on the first DCA axis. The second group, as evidenced by the curves, seemed to have the highest abundance at intermedi- ate scores on the first DCA axis. The plots for the individual species revealed, howev- er, that several of these species were found at variable abundance at all, or nearly all, axis scores. The group, therefore, includes species with no clear response to the factors underlying the axis. The shapes of the curves for these species appear somewhat arbitrary. The third group decreased in abundance with increasing site scores on the first DCA axis. The groups were nearly the same as those identified by the CCA plot (see above).
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