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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),

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