Fróðskaparrit - 01.01.1998, Side 21

Fróðskaparrit - 01.01.1998, Side 21
EIN OYGGJALÍVLANDAFRØÐILIG GREINING AV FLORUNI f FØROYUM 27 Koltur are among the smallest islands, and the model is probably less reliable for small areas. Nólsoy also deviates significantly (Table 2) and we are unable to account for the underlying cause. The model is directly misleading in the case of Koltur, which has as many as 108 species on its 2.5 km2 which according to the null hypothesis ‘should’ have held an estimated 51 species. In our opinion, the underlying causes are multiple. Koltur is a fertile island which would al- low for a higher number of species. Bengt- son and Bloch (1983) mention that Koltur is priced at 17 merkur from ancient times, whereas Hestur despite its more than dou- ble size is priced at only 18 mercur. Mork (pl.: merkur) is an old Faroese measure for soil fertility. If you study the island’s profile (Figure 3) it seems obvious that here must be many species. There is plenty of lowland and this is where the many species are found. But the island also has an intermediate zone, because Koltur reaches 479 metres despite its very limited area. Finally, the fine acces- sibility of the island has the effect that it was possible to find many species within the allocated time when the investigation was being conducted. One way to compare island flora The starting point in every comparison be- tween the flora or fauna of two regions must always be a list of the organisms of the regions. Subsequently, a measure is pre- sented - based on different criteria - as to how many different species occur in both regions. The subject is thoroughly de- scribed in e.g. Connor and Simberloff (1978). By the development and selection of a suitable similarity index, it has been a recurring problem to assess the indexes, and as often a biological null hypothesis has been missing. In the present section, we shall briefly in- troduce a way in which to compare the flo- rae of two regions - a similarity index, if you will. The method is based on the previ- ously described null hypothesis. The nature of the species as well as the total number of species are well-known for each of the islands. The number of common species for the two islands is also well- known, let us refer to that by the letter u. You can also calculate the number of com- mon species on the two islands based on the predictions of the null hypothesis in terms of which common species ‘ought’ to be on these two islands, considering their given areas. We shall call this figure v. If one island contains x species, the area Aj, which the island ‘ought’ to have ac- cording to the null hypothesis, is deter- mined. This also applies for the other island having y species and ‘area’ A2. The null hy- pothesis now gives the number of species anticipated, k, in a region of an area A,+A2 and v = x + y - k. u-v is thus an expression of whether the florae of the two islands are more or less similar than could be anticipated. But it is not possible to apply the expres- sion directly for comparisons, as the vari- ance differs from one pair of islands to an- other. In order to compensate for this, we have constructed a variance, see appendix. Table 3 shows a comparison of all 153
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