Soil and fumarole gases of Mount Etna: geochemistry and relations with volcanic activity
Introduction
Mount Etna is the largest volcano in Europe (∼1200 km2 of total surface with a maximum height of ∼3300 m above sea level) and is one of the most active in the world. The relatively easy access to its active areas makes it an ideal site for field volcanological studies. An enormous amount of data has so far been collected on Etna for a great number of volcanological parameters (e.g., Chester et al., 1985; GNV, 1990). However, remarkably few data are available on the chemistry of Etna's volcanic gases, especially those emitted from fumaroles (Le Guern, 1972; Huntingdon, 1973; Allard, 1983), mainly because of the absence of suitable sampling sites. Air contamination in the sampled gases is generally very high, due both to the high permeability of the loose pyroclastic materials which make up most of the soils of Etna's summit and to the low flux of the emitted gases as a consequence of their preferential drainage towards the nearby open summit craters. Therefore, in recent years the attention of geochemists has been focused on soil gases sampled on the lower flanks of the volcano. Many studies in the last ten years have shown that important soil degassing phenomena occur diffusely on peripheral areas of Etna along active tectonic structures, where CO2 is the most abundant species emitted (Aubert and Baubron, 1988; Allard et al., 1991; Anzà et al., 1989, Anzà et al., 1993; D'Alessandro et al., 1992; Giammanco et al., 1995, Giammanco et al., 1997; Parello et al., 1995; Baubron, 1996). The temporal variations in the concentrations of some of these soil gases, and in particular in the diffuse flux of CO2, have shown significant correlations with variations in volcanic activity (Giammanco et al., 1995; Parello et al., 1995; Giammanco and Inguaggiato, 1996).
The aims of the present study were to characterize the chemical and isotopic compositions of the gases emitted from the crater fumaroles and from the soils of Etna at various altitudes. Secondly, by repeating our sampling, we studied how the chemical and isotopic compositions of these gases can be affected by variations in volcanic activity.
Section snippets
Sampling and analytical procedures
Samples of soil and fumarole gases were collected at a depth of 50 cm through a 5-mm-ID teflon tube connected to a syringe and then stored in glass flasks equipped with vacuum stopcocks. Samples for isotopic analyses were passed through a tube containing lead acetate during sampling in order to eliminate H2S and water vapor. Chemical analyses were performed using a Perkin-Elmer 8500 gas chromatograph with argon as carrier gas and equipped with a 4-m Carbosieve S II column and double detector
Geochemical characterization of Etna's gases
The map in Fig. 1 shows the location of the sites on Etna where fumarole and soil gases were collected during the period 1993–1996. The fumaroles sampled were chosen among those having the highest outlet temperature (300 to 730°C); all other points were chosen among those with anomalous soil degassing. Point TDF is located a few tens of meters south of the Torre Del Filosofo hut (2750 m a.s.l.) on the southern flank. This site is characterised by anomalous degassing from the soil (CO2, Rn and
Temporal evolution of Etna's gases
Most of the measured geochemical parameters showed important variations during the period 1993–1996 (Table 1). In particular, the most evident changes were observed in the concentrations of H2, CO, CH4 and He, this latter only at point P39, as well as in the diffuse fluxes of CO2 through the soil. As an example, Fig. 5 shows the temporal variations of H2 concentration values in the soil gas samples and of CO2 fluxes through soils.
At least two strong increases in soil H2 concentration can be
Conclusions
The chemical composition of all the gases sampled on Mt. Etna seems to be the result of two basic physico–chemical processes (Fig. 6). The first is a mixing between a deep magmatic component, represented in the figure by the restored analyses of fumarole gas, and air (`air contamination' line in Fig. 6). The second process, more evident in the samples from point P39, consists of a apparent enrichment in He of the soil gas caused by dissolution of magmatic CO2 into a hydrothermal aquifer
Acknowledgements
The authors wish to thank Dr. Franco Parello for his help in analysing the isotopic composition of the collected CO2 samples and, together with Dr. Walter D'Alessandro, for providing important chemical and isotopic data on point P39. We also thank Dr. Franco Italiano for providing the He isotopic values relative to points P78 and P39, Drs. Giorgio Capasso, Walter D'Alessandro, Rocco Favara and Giovannella Pecoraino for revising the manuscript and Drs. Franco D'Amore and Donald M. Thomas for
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