Náttúrufræðingurinn

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Náttúrufræðingurinn - 1988, Side 23

Náttúrufræðingurinn - 1988, Side 23
Sigurjón Rist 1986. Efnarannsókn vatna. Borgarfjörður, einnig Elliðaár í Reykjavík. Orkustofnun, Reykjavík OS-86070/VOD-03. 46 bls. Stefán Arnórsson, Sven Sigurðsson & Hörður Svavarsson 1982. The chemist- ry of geothermal waters in Iceland. I. Calculation of aqueous speciation from 0° to 370°C. Geochim. Cosmochim. Acta 46. 1513-1532. Unnsteinn Stefánsson 1950. Meðalfells- vatn. Náttúrufrœðingurinn 20. 170-175. Unnsteinn Stefánsson & Björn Jóhannes- son 1978. Miklavatn í Fljótum. Nátt- úrufrœðingurinn 48. 24-51. Þorleifur Einarsson 1985. Jarðfræði. 5. út- gáfa, Mál og menning, Reykjavík. 233 bls. Walling, D.E. & B.W. Webb 1986. Solut- es in river systems. / Solute Processes (ritstj. S.T. Trudgill). John Wiley & Sons Ltd. New York. 251-327. Veðurstofa íslands 1958-1987. Mælingar á nokkrum efnum í úrkomu og andrúms- lofti. / Veðráttunni 1958-1987. SUMMARY Chemistry of rivers in Iceland and the rate of chemical denudation by Sigurður R. Gíslason and Stefán Arnórsson Science Institute University of Iceland Dunhagi 3 IS-107 REYKJAVÍK Iceland The rate of chemical denudation in Ice- land is at least two times that of the conti- nents. This is because of high precipita- tion and run-off and the abundance of re- active glassy basaltic rocks in Iceland. Temperature, discharge and total dis- solved solids are stable in spring-fed rivers but not in direct run-off and glacier-fed rivers. The pH of direct run-off rivers and glacier-fed rivers ranges from 7 to 7.5 and is controlled by the dissociation of the aqueous C02 species. The pH of the spring-fed rivers ranges from 8.5 to 9.5 and is controlled by the dissociation of the aqueous monomeric silica species. The spring waters are undersaturated with re- spect to the C02 of the atmosphere. At- mospheric C02 dissolves downstream in the spring-fed rivers and can simultan- eously lower the pH of the water. How- ever, the time available for the dissolution of atmospheric C02 is short, less than one day, so relatively short spring-fed rivers can maintain high pH all the way to the river mouth. The same applies for the dis- solution of suspended load in the main stream of the rivers. The time for dissolu- tion is less than a day, and therefore does not have a significant effect on the amount of total dissolved solids in the main stream. 197

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