Microbial biofilms control economic metal mobility in an acid-sulfate hydrothermal system

Trace metal cycling in hydrothermal systems has been the subject of a variety of geochemical and economical geology studies. Typically in these settings these elements are sequestered in sulfide and oxide mineral fractions, however in near-surface low-temperature environments organic matter and microorganisms (typically in mats) have been implicated in their mobility through sorption. Here we specifically examine the role of microbial biofilms on metal partitioning in an acid-sulfate hydrothermal system. We studied the influence of microorganisms and microbial biofilms on trace metal adsorption in Pailas de Aguas I, an acid-sulfate hot spring on the southwest flank of Rincon de la Vieja, a composite stratovolcano in the Guanacaste Province, Costa Rica. Spring waters contain high suspended loads, and are characterized by high T (79.6-89.3^oC), low pH (2.6-4), and high ionic strengths (I= 0.5-0.8). Waters contain high concentrations of the biogeochemically active elements Fe (4-6 mmol/l) and SO₄^2- (38 mmol/l), but PO₄^3- are below detection limits (bdl). Silver, Ni, and Mo concentrations are bdl; however other trace metals are present in solution in concentrations of 0.1-0.2 mg/l Cd, 0.2-0.4 mg/l Cr and V, 0.04-1 mg/l Cu,. Preliminary 16S rRNA analyses of microorganisms in sediments reveal several species of algae, including Galderia sp., Cyanidium sp, γ-proteobacteria, Acidithiobacillus caldus, Euryarcheota, and methanogens. To evaluate microbial biofilms' impact on trace metal mobility we analyzed a combination of suspended, bulk and biofilm associated sediment samples via X-ray diffraction (XRD) and trace element sequential extractions (SE). XRD analysis indicated all samples were primarily composed of Fe/Al clay minerals (nontronite, kaolinite), 2- and 6-line ferrihydrite, goethite, and hematite, quartz, and opal-α. SE showed the highest concentrations of Cu, Mo, and V were found in the suspended load. Molybdenum was found primarily in the residual and organic fractions of suspended sediments. Copper is distributed in all but the carbonate fraction of suspended sediments. Vanadium was bound primarily to the oxide and residual fractions with Si, which is probably found as opal-α. In contrast, biofilm sediments had the highest concentrations of Fe, Si, Cd, Al, Zn, Ag, and Ni. Trace metals were sequestered mainly in the organic fraction in decreasing concentrations of: Cu <Cr <Zn <Ag=Ni <Cd. The redox active element Fe occurs mainly in the oxide fraction. Phosphate and S present in the exchangeable fraction of all samples suggesting diagenitic or desorptive processes may be required to make it bioavailable. Intriguingly S was also abundant (11 mmol/l) in the organic fraction of biofilm sediments, which may be the result of sulfur oxidizing organisms generating elemental sulfur. Because trace metals are primarily bound in the organic fraction we posit that this may be a strategy by microorganisms to reduce metal toxicity in an acid environment through sequestration, making these metals relatively immobile until geochemical conditions dramatically changed. Similar patterns of trace metal partitioning into microbial biofilms have been observed in other acid systems, including acid mine drainage at Rio Tinto, Spain. Therefore, microbial sequestration of toxic metals may be a common coping mechanism in acid sulfate systems.