Náttúrufræðingurinn

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Náttúrufræðingurinn - 1998, Qupperneq 94

Náttúrufræðingurinn - 1998, Qupperneq 94
scape and land-use around Norwegian alu- minium smelters. Environm. Pollut. 8.113-121. Haukur Jóhannsson & Sigmundur Einarsson 1988. Krísuvíkureldar I. Aldur Ögmundarhrauns og Miðaldalagsins. Jökull 38. 71-87. Kristinn P. Magnússon 1984. Ahrif loftmengunar frá Alverinu í Straumsvík. Ritgerð við Líf- fræðiskor Háskóla Islands. Murray, F. 1981. Effects of Fluorides on Plant Communities around an Aluminium Smelter. Environm. Pollut., Ser. A 24. 45-56. Richardson, D.H.S. & Puckett, K.J. 1971. Sulphur Dioxide and Photosynthesis in Lichens. í: Ferry, B.W., Baddeley, M.S. & Hawksworth, D.L. (ritstj.), Air Pollution and Lichens. The Athlone Press of the University of London. Bls. 283- 298. SUMMARY Plant community changes around the ALUMINIUM SMELTER IN STRAUMSVÍK, ICELAND The aluminium smelter in Straumsvík, SW-Iceland, has been in operation since 1969. In 1980, fluoride emission from the smelter was 1100 tons/year on average. During the period 1982-1991 itdecreased to 500 tons/year and has since 1992 been approxi- mately 140 tons/year, as a result of improved cleaning system. Sulphur dioxide emissions have remained near 1500 tons/year on average the whole period 1980-1997. The normal vegetation of this lava field consists mainly of carpets of Racomitrium lanuginosum, with Empetrum nigrum ssp. hermaphroditum on exposed sites (Fig. 2). Sheltered depressions in the lava fields are characterized by heath vegetation, dominated by Calluna vulgaris, Empetrum nigrum ssp. hermaphroditum, Vaccinium uliginosum and Arctostaphylos uva-ursi (Fig. 1). Exposed lava peaks, sticking out above the Racomitrium carpet, are covered with lichens (Fig. 3), mainly Stereo- caulon vesuvianum, Pertusaria corallina, Ochro- lechia lactea and Porpidia melinodes. During the first 20 years of operation consider- able changes were observed in the vegetation within 1 km distance around the smelter. The vegetation has been severely affected by air pollutants closest to the factory. The Racomitrium carpets in 300 m distance have become black, like they are more or less bumed up (Fig. 8 and 9), the lichens are dead and the rock faces are bare (Fig. 7), but Empetrum nigrum has increased its coverage. In sheltered sites all dwarf shrubs have disappeared from the heath vegetation except Empetrum nigrum, which has in- creased from 16 to 70% coverage (Fig. 6). Vegetation analyses using the point quadrat method were made in these lava fields in the fall 1989. Two sites were selected in 300 m distance from the factory, one sheltered in a depression and the other exposed. For comparison, two similar sites were selected in 2 km distance from the fac- tory, where the vegetation appeared to be normal. The results of these analyses are shown in figs. 4— 6. At both sites the species diversity has declined considerably in 300 m distance, as compared with 2 km distance from the smeltcr (Fig. 11). It is remarkable how resistant Empetrum nigrum seems to be, the only surviving dwarf shmb in 300 m distance from the factory. It not only survives, but even increases its cover substantially as it colo- nizes the area left by the declining Racomitrium carpets. However, it was noticed that while the air pollution didn’t affect its reproduction, the older branches were damaged after several years of expo- sure, as seen in fig. 6. Similar experience has been reported near alu- minium smelters in northem Norway (Gilbert 1975), where Calluna vulgaris in a dwarfshmb heath was replaced by Empetrum nigrum and Salix repens. In that case the lichens and the bryophytes were also heavily damaged. As a result of this investigation, the following general conclusions were made: 1. Damage of vegetation is primarily to be ex- pected on exposed surfaces like hills, cliffs, lava peaks or on trees. 2. Damage of vegetation occurs mainly on the side facing the source of pollutants. 3. Most damage is to be expected in the direc- tion of prevailing winds from the origin of pol- lutants. 4. Bryophytes and lichens are much more af- fected than grasses and flowering plants sheding their leaves every year. 5. Individual species of these plant groups re- act to a different extent to the exposure to pol- lutants. PÓSTFANG HÖFUNDAR/AuTHOr's AdDRESS Hörður Kristinsson Náttúrufræðistofnun Islands/ Icelandic Institute of Natural History Pósthólf/P.O.Box 180 IS-602 Akureyri Netfang/E-mail hkris@nattfs.is 252
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