Full-text - Norsk entomologisk forening
Full-text - Norsk entomologisk forening
Full-text - Norsk entomologisk forening
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Norwegian stoneflies 11 245<br />
compacta often dominate high-altitude<br />
streams, sometimes together with Amphinemura<br />
standfussi. In lakes Capnia atra and<br />
Diura bicaudata usually dominate, although<br />
sometimes with N emurella pieteti, N emoura<br />
cinerea, or N emoura avicularis. In the southern<br />
areas Capnia atra is absent and there<br />
Diura bicaudata and N emurella picteti are<br />
often most numerous. In northern Norway<br />
Capnia atra and Diura bicaudata may dominate<br />
the fauna of both lakes and streams.<br />
According to Rauser (1971), the Taeniopteryx<br />
nebulosa and lsoperla obscura are<br />
characteristic for lentic currents of the<br />
boreal zone. In the streams west of Oslo<br />
which Rauser says belong to this type, I soperla<br />
obscura has not been recorded at all.<br />
If the species is present there, it is rare, and<br />
not characteristic. Even T aeniopteryx nebulosa<br />
is not characteristic for this stream type,<br />
as the species is just as common in stony<br />
streams with moss vegetation in the mountain<br />
areas.<br />
Finally Diura nanseni should be the characteristic<br />
carnivore stonefly species of the<br />
hilly-land and piedemont currents of the<br />
boreal zone, and not the Dinocras cephalotes<br />
mentioned by Rauser. Dinocras cephalotes is<br />
only found in isolated localities. Thus the<br />
above examples serve to show that Rauser's<br />
(1971) system for the northern areas is invalid.<br />
Attempts to use the systems presented by<br />
Hynes (1941) and Brinck (1949) for the<br />
Norwegian fauna have also had little success.<br />
Brinck (1949) divided habitats into spring,<br />
trickles, small eutrophic forest streams, southern<br />
streams, northern streams, southern rivers,<br />
northern rivers, jokks, ponds, southern lakes<br />
and northern lakes. He also stated that the<br />
classification based on different perceptible<br />
environmental conditions only serves as long<br />
as there is a true correlation between the<br />
species and the habitats, i.e. a habitat which<br />
does not correspond to a specific zoom has<br />
no authorization in the classification. Most<br />
of the Norwegian landscape is quite different<br />
from the Swedish, and this certainly makes<br />
the environmental factors act differently in<br />
Norway and in Sweden by producing another<br />
faunal association out of the total environmental<br />
impact on each species. Not all the<br />
habitats listed by Brinck (1949) fit well into<br />
the Norwegian landscape. This is illustrated<br />
by reference to western Norway, where high<br />
mountains provide cold water from melting<br />
snow for most of the summer. The water<br />
flows down into the lowlands which have a<br />
more or less atlantic climate. According to<br />
Brinck's (1949) classification, most of the<br />
larger streams have temperatures which fit<br />
well into the jokk type. Along much of their<br />
length they would also be of the jokk type<br />
regarding substratum and stream velocity,<br />
but between these parts there are still flowing<br />
silting sections at all attitudes. Faunistically,<br />
however, they do not belong to either the<br />
jokks or the northern streams. Typical inhabitants<br />
of the jokks, Capnia atra and Arcynopteryx<br />
compacta, are absent in the southern<br />
parts and the streams do not have the<br />
same association of species which are typical<br />
for the northern streams of Brinck (1949).<br />
Variation along the length of a single<br />
watercourse is most pronounced in western<br />
Norway, but also occurs in most other areas<br />
of the country. Therefore no attempt will<br />
be made in this study to classify streams.<br />
Ulfstrand (1968) discussed the classification<br />
of lotic biotopes and their animal communities<br />
and made the following classification:<br />
1. The biotope classification, where he<br />
concluded that a substratum classification<br />
was the most suitable. 2. The community<br />
classification. He mentioned the attempt made<br />
by Berthelemy (1966) to adopt faunistic criteria<br />
in his studies. These were largely unsuccessful<br />
and he concludes 'Community classification,<br />
based on characteristic species or<br />
species constellations (f. Berg 1948) will generally<br />
have only regional applicability'. In the<br />
present work Lufstrand's (1968) conclusion is<br />
reinforced by the faunistic differences observed<br />
in the seven investigated areas of<br />
Norway and the considerable differences in<br />
the biotope preferences of the species in northern<br />
and southern Norway indicate that generalizations<br />
should be avoided where possible.<br />
THE STONEFLY FAUNAS OF<br />
DIFFERENT AREAS GROUPED<br />
ZOOGEOGRAPHICALLY<br />
The zoogeography of stoneflies has been discussed<br />
by authors such as Brinck (1949),