Fróðskaparrit - 31.12.2000, Qupperneq 117

Fróðskaparrit - 31.12.2000, Qupperneq 117
TITTLEIKIN AV VANLIGASTU FØROYSKU DýRA- OG TARASLØGUNUM A KLETTASTRONDI MUN TIL YMISK UMHVØRVISVIðURSKIFTI 121 tude larger than 0.4 m implied that at low wave exposure levels another factor was of importance. This was not reflected in the CCA plot, and the axis was only weakly correlated with any environmental variable (negatively with the exposure index and positively with the substrate index). The in- terp'retation of this axis may only be specu- lated. It may have reflected a different as- pect of exposure, for instance a different time aspect, than the first axis. From the species plot, it seemed that the axis may have reflected life-history pattems, with temporally stable, long-lived species such as Ascophyllum nodosum and Corallina of- ficinalis at the top of the diagram, and tem- porally more variable and potentially op- portunistic species such as Fucus evane- scens at the bottom of the diagram. This might be connected to the particular histo- ries of the sites, but needs further exploring. Biotic factors The results indicated that direct effects of grazing by Littorina or Patella, or preda- tion by Nucella could not explain any large part of the variation in the ordination. How- ever, as already pointed out, such interac- tions may surely have occurred, as known from experimental studies elsewhere (see e.g. Hartnoll and Hawkins, 1985; Chap- man, 1995). but their effects were not pro- nounced with the scale and sampling method used. Indirect effects of grazing could not be ruled out as a possible expla- nation for some of the variation. If so, these effects caused a similar species pattern to that caused by wave exposure. It was not possible to say to what extent competition between species influenced the observed patterns. The degrees of distributional over- laps along the gradient were indicated by the distances between the species centroids in the DCA plot (Fig. 3) as well as by com- parisons of the plots of species abundances versus site scores on the first DCA axis (Fig. 4). For instance, the centroids of Fu- cus distichus ssp. anceps and Ascophyllum nodosum were distanced far apart in the DCA plot, suggesting little distributional overlap, which was further confirmed by the plots of their abundances along the first DCA axis, from which it seemed that the two species did not occur together at all. Such pattems might be induced both by ex- trinsic factors such as wave exposure as well as by interactions between the species, or perhaps most likely, by a combination of both. Experimental studies are needed to discern the causative factors for the distrib- utions. Species abundance curves Considering the discussion of the factors influencing the first DCA axis for sites with tidal amplitude larger than 0.4 m, it seems reasonable to interpret the plots of species abundance versus site scores on the axis as the species responses to wave exposure. The three groups identified were, thus, (1) species that increase in abundance with in- creasing exposure, (2) species with abun- dance optimums at intermediate exposure or with no clear response to exposure, and (3) species that increase in abundance with decreasing exposure.
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