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Alkaline sulphate fluids produced in a magmatic hydrothermal system

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Comparison of SO 2− 4 as determ<strong>in</strong>ed by ICP-AES (as total sulphur; SO 2− 4 should be the<br />

dom<strong>in</strong>ant species <strong>in</strong> acidified samples) and IC showed significant discrepancy between the<br />

two techniques, particularly for 2006 hot spr<strong>in</strong>gs, with SO 2− 4 concentrations lower when<br />

determ<strong>in</strong>ed by IC. Sulphate content was also measured by gravimetry of barium <strong>sulphate</strong><br />

precipitated from acidified samples <strong>in</strong> the field (see Section 3.2). Sulphate contents<br />

determ<strong>in</strong>ed by gravimetry were similar to ICP-AES data, rather than IC data, suggest<strong>in</strong>g that<br />

the <strong>sulphate</strong> <strong>in</strong> the latter (unacidifed) samples had been subject to modification, either by<br />

bacterial reduction or m<strong>in</strong>eral precipitation. Logistical constra<strong>in</strong>ts meant that time between<br />

sampl<strong>in</strong>g and analysis was over one month. Consequently, ICP-AES data for SO 2− 4 are used<br />

<strong>in</strong> preference to results obta<strong>in</strong>ed by IC.<br />

Charge balance error (CBE) was calculated for major species (H + , Al 3+ , Fe 2+ , Ca 2+ , K + , Mg 2+ ,<br />

Mn 2+ , Na + , SO 2− 4 , Cl − , HCO − 3 ). Total carbonate is presented as HCO − 3 equivalent, and is<br />

calculated as a monovalent anionic species for the purposes of charge balance. High CBE<br />

may occur due to <strong>in</strong>appropriate choice of valency for carbonate species (i.e. if carbonate<br />

species are dom<strong>in</strong>ated by CO 2− 3 , rather than HCO − 3 ). Charge balance error is higher for 2005<br />

samples as no carbonate analyses were made. For samples where all major species have been<br />

<strong>in</strong>cluded, CBE should ideally be with<strong>in</strong> ±5%.<br />

3.2 Sulphur Isotopes<br />

For aqueous <strong>sulphate</strong> analysis, 75 ml (100 ml for 2006 samples) of filtered sample was<br />

decanted <strong>in</strong> the field <strong>in</strong>to a HDPE bottle, acidified with 1 ml Tracepur ® 69% HNO 3 , and an<br />

excess of 5% BaCl 2 solution was added slowly to precipitate BaSO 4 . In the laboratory,<br />

precipitated BaSO 4 was separated from the water by centrifuge, r<strong>in</strong>sed with deionised water,<br />

dried at 80°C overnight, and weighed to determ<strong>in</strong>e SO 2− 4 concentration. These data were<br />

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