The Extremes of the Extremes: Extraordtnaiy Floods (Proceedings of a symposium held al Reykjavik. Iceland. July 2000). IAHS 1'ubl. no. 2 7 1 . 2002. 223 Seasonal variation in the chemistry of glacial-fed rivers in Iceland HREFNA KRISTMANNSDÔTTIR Orkustofnun, Grensâsvegur 9, IS-IOS Reykjavik, Iceland e - m a i l : hk(ojos.is SIGURDUR R. GISLASON Science Institute, University of Iceland, Dunhagi 3, IS-107 Reykjavik, Iceland ÂRNI S N O R R A S O N Orkustofnun. Grensâsvegur 9, IS-IOS Reykjavik. Iceland HREINN H A R A L D S S O N Public Roads Authority, Borgarti'tn 5, IS-105 Reykjavik, Iceland STEINUNN H A U K S D Ô T T I R & ASGEIR G U N N A R S S O N Orkustofnun, Grensâsvegur 9, IS-IOS Reykjavik, Iceland Abstract Ten Icelandic rivers have been monitored at 11 sites throughout one year to obtain baseline values for the design of warning systems based on chemical changes preceding subglacial volcanic eruptions. Seasonal changes characteristic of each river have been identified as well as alarm values for chosen parameters. Six pilot systems based on the measurement of conduct ivity have been put into operation and run for several months. The conductivity of water at the sites varies from 20 to more than 300 pS cm" between rivers and seasons. During jôkulhlaups, conductivity may exceed 700 uS cm" . Other potential parameters to monitor for warning purposes are hydrogen sulphide and mercury. Tests have been run collecting data on those substances for continuous measurement, but practical methods to operate such stations have not yet been developed. 1 1 K e y w o r d s s e a s o n a l v a r i a t i o n ; glacial r i v e r s ; m o n i t o r i n g ; v o l c a n i c ; g e o t h e r m a l ; j ô k u l h l a u p ; subglacial eruption; conductivity; mercury; hydrogen sulphide INTRODUCTION Prior to a major flood caused by volcanic activity or increased geothermal activity, changes in the chemistry of the glacial river water may be detected (Kristmannsdôttir et al, 1999, Kristmannsdôttir, 2 0 0 1 ; Gislason et al, 1998; Snorrason et al, 1997). For chemical precursors to be detected, the seasonal changes in the chemistry of the river in question must be well documented. Furthermore, the changes due to volcanic activity and/or increased geothermal activity must be known (Kristmannsdôttir et al, 2002). The seasonal changes in chemical composition of the rivers and possible effects due to continuous geothermal activity below the glacier on the water chemistry was poorly known prior to the present study. Conductivity had been measured regularly in the Skeiôarâ River through the period 1990-1991 for monitoring purposes, but in no other glacial river prior to the 1996 volcanic eruption in the Vatnajôkull Glacier. The 224 Hrefna Kristmannsdôttir et al. 10 20 30 40 60 km Fig. 1 The location of the rivers monitored in the project. Jôkulsâ â Sôlheimasandur River draining the Myrdalsjôkull Glacier (Fig. 1) had been sampled several times for chemical analysis, and chemical monitoring of some parameters had also been pursued intermittently during the last 20 years. Nevertheless, no basis for an effective warning system had been defined. Almost no data existed from other rivers draining the Myrdalsjôkull Glacier prior to the project described in this paper. After the subglacial volcanic eruption in the Vatnajôkull Glacier and prior to the subsequent catastrophic flood from the Grimsvôtn subglacial lake, regular measure ments of discharge and conductivity were earned out to monitor the development of the flow of water from the Grimsvôtn subglacial lake (Snorrason et ai, 1997). These measurements showed clearly, in retrospect, that changes in conductivity could be used as a predictor for a flood. After the events of 1996 a project was initiated with the aim Seasonal variation in the chemistry of glacial-fed rivers in Iceland 225 of developing an automatic warning system for volcanic eruptions based on monitoring changes in glacial river chemistry. The first phase of the project was aimed at obtaining background data to establish the seasonal changes in glacial water chemistry and selecting the parameters to be monitored. Furthermore, the alarm values for each parameter in the different rivers were to be defined. The second phase of the project was to develop an automatic warning system and to run it experimentally in a few rivers for at least one year (Elefsen et al, 2001). This paper reports the results of the first phase of the project which entailed chemical monitoring of 10 selected glacial rivers discharging from the Vatnajôkull Glacier and the Myrdalsjôkull Glacier in Iceland. SCOPE O F T H E PROJECT Due to cost, the number of sampling sites as well as the frequency of sampling had to be restricted. Therefore, water samples were collected once a month for one year from 11 selected sampling sites according to the practice of the geochemical laboratories of Orkustofnun and the Science Institute at the University of Iceland. Discharge of the rivers as well as sediment load were measured at the same time. The rivers monitored (Fig. 1) were: The Skjâlfandafljôt River, the Jôkulsâ â Fjôllum River at Grimsstaôir and at Upptyppingar, the Kreppa River, the Skeiôarâ River, the Gigja River, the Sûla River, the Djûpâ River, the Skaftâ River at the Âsa-Eldvatn, draining from the Vatnajôkull Glacier, and the Mûlakvisl River and the Leirâ River draining from the Myrdalsjôkull Glacier. The components monitored were: total dissolved solids (TDS), pH, total carbonate, Ff S, main dissolved solids (SiOa, Na, K, Ca, Mg, Cl, SO4), selected trace elements and heavy metals (F, B, Br, Al, Cr, Mn, Fe, Cu, Zn, As, Cd, Hg, Pb), and the isotopes ôD, 8 0 , 8 C . Samples were taken for the measurement of apparent C age, but so far funding has not been obtained for their analysis. 2 1 8 I3 l 4 Conductivity was measured more frequently at two of the sampling sites, approximately twice a week, during the project. In the Jôkulsâ River at Grimsstaôir, conductivity monitoring started in December 1996 and was continued until a pilot station for continuous measurement of conductivity was started in May 1999. In the Skeiôarâ River, conductivity was measured routinely from October 1996 with a few interruptions until a pilot station for continuous measurement of conductivity was started there in December 1998. RESULTS The seasonal changes in the rivers are well demonstrated by the changes in total concentration of dissolved solids as well as by conductivity (Fig. 2). The measured conductivity varied between 20 and 300 |iS cm"' and TDS between 10 and 170 mg" , and values were higher in the samples influenced by jôkulhlaups, where conductivity may exceed 700 (iS cm" . During the monitoring period, there was a jôkulhlaup in the Skeiôarâ River, and geothermal water leaked into the river from the subglacial lake at Lake Grimsvôtn for most of the time (Fig. 3). Two jôkulhlaups also occurred in the Skaftâ River during the monitoring period. All the waters are classified as sodium 1 1 226 Hrefna Kristmannsdôttir et al. Seasonal variation in the chemistry of glacial-fed rivers in Iceland Scp-96 Dec-96 Mar-97 May-97 Aug-97 Nov-97 Feb-98 May-98 227 Aug-98 Nov-98 Fig. 3 Conductivity measurements in the Skeiôarâ River during the monitoring period. bicarbonate type waters of very low TDS with pH typically 7.2-8.0. In the rivers influenced by geothermal water, increased concentrations of sulphate and calcium are noted, and pH may either drop or increase depending on the length of the flowpath (Kristmannsdôttir et ah, 1999). Silica is typically 5-20 m g l" under normal conditions. In the rivers like the Leirâ River and the Mulakvisl River with much geothermal influence, the silica may reach 40 m g l" and even higher during jôkulhlaups as in the Skeiôarâ River. Sulphide is not detected in the waters except in rare cases in water from jôkulhlaups. Mercury is mostly below detection of 1-2 ng l" and when detected it is in the range of about 10-20 ng l" . The concentrations of other heavy metals are very low. The concentrations of nutrient salts (NO3, NO2, N H , PO4) are generally very low but variable. 1 1 1 1 3 CONCLUSION There are clear relationships between discharge and the chemical composition of the river water, but the correlations are different among the rivers (Fig. 4). Interpretation of chemical data and flow rates suggests two main components of river water: water that has reacted with the subglacial bedrock for some time, and meltwater with much lower TDS (Kristmannsdôttir et al., 1999). In some rivers, there is also a third comp onent originating from subglacial geothermal systems. In some of the monitored rivers, 228 Hrefna Kristmannsdôttir et al. o Âsa-Eldvatn Djûpâ -0<>0 O " o % • 0 O O O o o o 1 f i 1 1 1 1 1 1 r 1 0 1 1 o 1 1 1 1 1 o 200 Gigja 80 1 ° o o 3 Cîi'imxslaAir @ Upptyppingar Jôkulsâ â Fjôllum O o •» - O o > U • - O 3- E u O o - • o o 40 O T3 C O o 1 1 1 1 I I ! I 40 Kreppa 1 1 o 200 Leirâ " oo . o o I I I I I I I I I I I o - O -J o I I I È I I o 20 40 60 80 100 120 140 160 O o I_ 1 1 0 O ° 180 200 1 1 0 Mûlakvisl Skeiôarâ o o -O o _o _o o o o - o o o o o O o - o o o o 1 0 1 20 1 1 40 1 1 60 1 1 80 1 100 0 o 1 o 1 200 Fig. 4 Data for discharge and conductivity of water in different rivers. o 1 Seasonal variation in the chemistry of glacial-fed rivers in Iceland 229 for example, the Leirâ River and the Mulakvisl River, the geothermal component is more or less continuously discharged into the rivers; in others like the Kreppa River, it is seasonally dependent; and in others like the Skeiôarâ River and the Skaftâ River, it only appears during jôkulhlaups or leakages from ice dammed or subglacial lakes formed by geothermal activity. In all the rivers, subglacial volcanic eruptions may affect the chemistry of the water, and to be able to detect them, the relative influences and ranges of each of the other three components has to be known. Most main components e.g. TDS, Na, Ca, K, CO2 (tot), and CI, as well as conductivity, could be used to monitor increased influence of geothermal/volcanic activity on glacial water chemistry. Of these, conductivity is the most easily measured. Mercury and some sulphur species are the most significant special parameters not occurring under normal conditions. However, a practical solution for the operation of monitors for these constituents has not been developed. Based on the monitoring results, alarm values of maximum conductivity vs flow rate have been defined. Six pilot stations monitoring conductivity (Elefsen et ai, 2002) are already in operation as a result of the project. REFERENCES Elefsen, O. S., Snorrason, Â., Haraldsson, H., Gislason, S. R. & Kristmannsdôttir, H. ( 2 0 0 2 ) Real-time monitoring of glacial rivers in Iceland. In: The Extremes ofthe Extremes: Extraordinary Floods (Proc. Reykjavik Symp., July 2 0 0 0 ) (ed. by Â. Snorrason, H. P. Finnsdôttir & M. M o s s ) . I A H S Publ. no. 271 (this volume). Gislason, S. R., Snorrason, Â., Kristmannsdôttir, II. & Svcinbjôriisdôttir, Â. E. ( 1 9 9 8 ) T h e 1996 subglacial eruption and flood from the Vatnajôkull glacier, Iceland: effects of volcanoes on the transient C O : storage in the ocean. Mineral Mag 6 2 A , 5 2 3 - 5 2 4 . Kristmannsdôttir, H., Bjôrnsson, A., Pâlsson, S. & Sveinbjôrnsdôttir, À. E. ( 1999) T h e impact of the 1996 subglacial volcanic eruption in Vatnajôkull on the River Jôkulsâ â Fjôllum, N o r t h Iceland. J. Volcan. Geotherm. Res. 9 3 , 3 5 9 372. Kristmannsdôttir, H. (2001) Interactive processes due to subglacial volcanic activity: local p h e n o m e n a with global c o n s e q u e n c e s . Water-Rock Interaction 2001 (ed. by Cidu), 3 7 - 4 6 . Sweets & Zeillingcr, Lisse. Kristmannsdôttir, H., Snorrason, Â., Gislason, S. R., Haraldsson, H., G u n n a r s s o n , Â., Hauksdôttir, S. & Elefsen, S. O. ( 2 0 0 2 ) Geochemical w a r n i n g for subglacial e r u p t i o n s — b a c k g r o u n d and history. In: The Extremes ofthe Extremes: Extraordinary Floods (Proc. Reykjavik S y m p . , July 2 0 0 0 ) (ed. by À. Snorrason, H. P. Finnsdôttir & M. M o s s ) . I A H S Publ. no. 271 (this volume). Snorrason, Â., Jônsson, P., Pâlsson, S., Ârnason, S., Sigurôsson, O., Vikingsson, S., Sigurôsson, Â. & Z ô p h ô n i a s s o n , S. ( 1997) Hlaupiô â Skeiôarârsandi haustiô 1996—ûtbrciôsla, rennsli og aurburôur (The j ô k u l h l a u p in Skeiôarârsandur in the fall of 1996—Extent of inundation, discharge and sediment transport) (in Icelandic). In: Vatnajôkull—Gos og Hlaitp 1996 (Vatnajôkull—Eruption and Jôkulhlaup 1996) (ed. by H. Haraldsson), 7 9 - 1 3 7 . T h e Icelandic Public Road Administration, Reykjavik, Iceland.
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