The effect of adsorbed lipid on pyrite oxidation under biotic conditions

Abstract

The effect of adsorbed lipid on pyrite oxidation under biotic conditions

Jun Hao1, Curtis Cleveland1, Eelin Lim2, Daniel R Strongin1,3 and Martin AA Schoonen3

1Department of Chemistry, Temple University, Philadelphia, PA 19122, USA

2Department of Biology, Temple University, Philadelphia, PA 19122, USA

3Center for Environmental Molecular Science, Stony Brook University, Stony Brook, NY 11794-2100, USA


Geochemical Transactions 2006, 7:8doi:10.1186/1467-4866-7-8. [Open Access]

Abstract

The chemolithoautotrophic bacterium, Acidithiobacillus ferrooxidans, commonly occurs in acid mine drainage (AMD) environments where it is responsible for catalyzing the oxidation of pyrite and concomitant development of acidic conditions. This investigation reports on the growth of this bacterial species on the pyrite surface and in the aqueous phase at a pH close to 2 as well as the role of adsorbed lipid in preventing pyrite dissolution. Both acid washed pyrite and acid-washed pyrite coated with lipids were used as substrates in the studies. The choice of lipid, 1,2-bis(10,12-tricosadiynoyl)-sn-Glycero-3-Phosphocholine lipid (23:2 Diyne PC), a phosphocholine lipid, was based on earlier work that showed that this lipid inhibits the abiotic oxidation rate of pyrite. Atomic force microscopy showed that under the experimental conditions used in this study, the lipid formed ~4–20 nm layers on the mineral surface. Surface-bound lipid greatly suppresses the oxidation process catalyzed by A. ferrooxidans. This suppression continued for the duration of the experiments (25 days maximum). Analysis of the bacterial population on the pyrite surface and in solution over the course of the experiments suggested that the pyrite oxidation was dependent in large part on the fraction of bacteria bound to the pyrite surface.


Background

It is well-known that several species of prokaryotes are able to catalyze the oxidation of pyrite and play an important role in the development of Acid Mine Drainage (AMD), a severe environmental problem. Acidithiobacillus ferrooxidans, for example, utilize reduced Fe2+ in AMD environments as an electron donor for energy production at low pH [1]. Due to the importance of microbes in the chemistry of such environments, a significant amount of research activity has been focused on understanding the role of microbes in the oxidation of sulfur-bearing minerals such as pyrite [2-11]. With regard to microbial-induced pyrite oxidation it is the general consensus that these microorganisms exert their impact on pyrite dissolution to a large degree by increasing the amount of available Fe3+ reactant [i.e., convert Fe2+ to Fe3+], which increases the rate of pyrite oxidation [3,12,13]. A goal of our research was to build on this prior research and to extend our understanding of microbial-accelerated pyrite oxidation to surfaces having adsorbed organic layers. With regard to this last point, the inhibition of pyrite oxidation using lipid having two hydrophobic tails (per polar head) has been studied as an AMD abatement strategy [14-16]. However, the lipid-induced inhibition of pyrite oxidation in the presence of microbes relevant to AMD has not been investigated. Toward this end, the experiments reported here were designed to investigate the effect of A. ferrooxidans microorganisms on pyrite oxidation in the presence and absence of adsorbed lipid layer at a solution pH near 2.

Our studies show that surface-bound lipid inhibits the oxidation of pyrite, even in the presence of bacteria. The lipid layers that suppress the oxidation limit the colonization of the bacteria on the pyrite, compared to lipid-free samples. This effect is observed throughout the duration of the experiment (about 25 days in all cases). Hence, in the presence of A. ferrooxidans the lipid coating remains in tact for at least 25 days and probably much longer. Furthermore, our study supports the notion that the rate of pyrite oxidation process is significantly controlled by the bacteria that colonize the pyrite surface.


Experimental methods

Pyrite pretreatment followed protocols, described in earlier work, [15] to generate clean pyrite (~10 μm average diameter) powder with a surface area of 0.75 m2/g. In brief, pyrite samples were crushed and subsequently acid washed using 0.1 M HCl. Acid washing of the pyrite was carried out by flowing pH 2-deoxygenated water over the mineral powder [14].

A pure culture of A. ferrooxidans (ATTC 23270) was obtained from the American Type Culture Collection (Manassas, VA). The culture was grown and maintained in ATCC #2039 broth as suggested by the supplier. Briefly, the medium consisted of two separately prepared solutions: Solution A contained 0.8 g (NH4)2SO4, 2.0 g MgSO4·7H2O, 0.4 g K2HPO4, 5.0 mL Wolfe's Mineral Solution, and 800 mL distilled water, adjusted to pH 2.3 with H2SO4 and then filter-sterilized. Solution B contained 20.0 g FeSO4·7H2O and 200.0 ml distilled water, which was filter-sterilized and then mixed with Solution A (above) to produce the complete medium. Cultures (9 ml) for experiments were grown unshaken using 100 ml of the medium in 250 ml Erlenmeyer flasks (autoclaved at 126°C and 20 psi for 0.5 h prior to use) at 25°C. The cultures were stoppered with nylon wool wrapped with aluminum foil.

For the experiments, A. ferrooxidans was grown to the early stationary phase of growth and harvested by a series of filtrations. First, the bacteria were separated from particulate material, which are presumably iron hydroxide particles in the media, by filtration through a 5-μm pore size polycarbonate filter (Millipore™). Second, the bacteria in the filtrate were collected on a 0.2 μm polycarbonate filter by vacuum filtration and resuspended in sterile water [pH 2.3] by vortexing. The amount of nutrients in this cell suspension (carried over from the culture) was 1% of the original concentration. This low nutrient concentration was necessary to minimize the impact of aqueous phosphate on pyrite oxidation [17]. Nevertheless, the concentration of nutrients present was sufficient to support growth of the bacteria in the presence of pyrite.

Lipid solutions were prepared by techniques described elsewhere [14]. In the current study, 0.1 g of acid washed pyrite was added to lipid solution (20 ml). The lipid solution contained 7.5 μmol of 23:2 Diyne PC lipid (Avanti Polar Lipids), which has the following structure:

07090902m01.gif

This particular concentration of lipid was chosen on the basis of prior research in our laboratory, and it was sufficient to cover the majority of the pyrite surface [14]. After 1 hour of mixing, the pyrite slurry was allowed to settle and the supernatant, which contained free lipid, was subsequently removed by decanting. The remaining fraction of lipid-coated pyrite slurry was used in the experiments.

The experiment was performed on two separate dates (from here on referred to as Experiment 1 and 2). The experimental conditions, treatments and analyses for both experiments were identical with the exception of the starting bacterial densities (see below). The treatments consisted of: 1) pyrite, 2) lipid-coated pyrite, 3) pyrite + bacteria, 4) lipid-coated pyrite + bacteria. All the treatments were prepared, in duplicate, in distilled water (pH 2.0) for a total volume of 50 ml. The treatments with pyrite contained 0.1 g of pyrite. Approximately the same amount of pyrite was present in the pyrite/lipid treatments (see preparation of lipid-coated pyrite slurry described above). The final density of A. ferrooxidans in the treatments with bacteria was approximately 3.3 × 107cells/ml for Experiment 1 and 1.7 × 107cells/ml for Experiment 2. Each treatment mixture was stirred continuously (using a teflon coated stir bar) throughout the experiment, which lasted a maximum of 25 days. Aliquots (1 ml) were withdrawn every 2–3 days for cell count analysis and preserved in 3.7% formaldehyde. In addition, 0.1 ml aliquots were withdrawn to determine the iron concentration in solution, which was used as a reaction progress variable. Total iron solution concentration determinations (including ferrous and ferric iron) were determined spectrophotometrically by using the ferrozine technique (UV method 8008). Since this technique is intrinsically sensitive to the concentration of ferrous, ascorbic acid was added to the solution prior to analysis to reduce any ferric to ferrous. All the sample aliquots for the ferrozine test were filtered through a 0.2 μm polycarbonate filter before analysis. Solution pH measurements were carried out with a PHM82 standard meter with a resolution of 0.01 pH units.

Enumeration of bacterial cell densities in solution and on pyrite powder were performed by epifluorescence microscopy following staining with the fluorochrome dye, acridine orange (AO) [18,19]. Briefly, preserved water samples were vacuum filtered onto 0.2-μm-pore-size blackened polycarbonate filters (Nuclepore) and the cells collected on the filter were stained with AO at a final concentration of 0.01% for 3 min. The volume of sample filtered for cell counts was chosen such that the layer of pyrite particles that accumulated on the filter would not obscure the bacteria. Cells were observed and counted with a Zeiss standard microscope equipped for epifluorescence microscopy. Filter sets used for AO fluorescence observations are as follows: a BP450-490 exciter filter, and FT510 chromatic beam splitter, and an LP520 barrier filter. For each sample, the number of bacteria on 10 to 15 randomly chosen fields distributed over the filter (or approximately 300 to 600 cells in total per filter) was counted. To determine the number of cells bound to pyrite, 0.1 ml aliquots (initial total volume was 50 ml) of the bacteria/pyrite solutions were collected on a 5 μm polycarbonate membrane filter (Millipore). The particles were subsequently washed so that any bacteria in solution would pass through the filter. The density of cells on the particulate material remaining on the filter was then determined using the staining method described above.

Surfaces for AFM were prepared from pyrite cubes (Navajun, Spain) obtained from Ward's Natural Science. Growth surfaces were cut from the cube and were subsequently polished. Prior to an experiment, the samples were exposed to pH 2 water (by HCl addition) to remove oxidized layers prior to exposing to lipid solution. To prepare the lipid/pyrite samples the pyrite platelet was submerged into the lipid solution in a vertical orientation (via a leading edge). The sample was then immediately removed, washed with pH 2 water to remove any loosely bound lipid, and then reintroduced to pH 2 water for imaging with a PicoSPM II (Molecular Imaging) microscope. The probes used in all the AFM measurements [NSC15, μMasch] had a nominal spring constant of 40 N/m and a resonant frequency of 325 kHz.


Results and discussion

It is generally accepted that both dissolved molecular oxygen and aqueous Fe3+ play a role in the oxidation of pyrite [12,20]. The overall composite reactions for pyrite oxidation in the presence of both these oxidizing agents can be expressed as follows:

FeS2 + (7/2)O2 + H2O → Fe2+ + 2SO4 2- + 2H+     (1)

FeS2 + 14Fe3+ + 8H2O → 15Fe2+ + 2 SO4 2- + 16H+     (2)

Prior studies of pyrite oxidation have shown that Fe(III) is a more aggressive oxidant of the pyrite surface than dissolved molecular oxygen [21,22]. Under strictly abiotic conditions, however, the concentration of Fe3+ in solution is relatively low, due to the slow oxidation kinetics associated with the conversion of Fe2+ product [see Eqn. (1)] to Fe3+ by dissolved O2. Hence, the contribution of eqn. (2) to pyrite oxidation under abiotic conditions is limited by the rate of ferrous iron oxidation, which is low in pH 2 solutions [21]. It is precisely this slow abiotic oxidation step that is catalyzed by microbes, such as A. ferrooxidans. The subsequent oxidation of the mineral by the aqueous Fe3+ is referred to as the "indirect" mechanism of pyrite oxidation [20]. This mechanism is in contrast to the "direct" mechanism, that involves the oxidation of the pyrite by surface colonized bacteria (either by enzymatic or non-enzymatic means) [8,20].

Data plotted in Figure 1 exhibits the influence of bacteria on the rate of pyrite oxidation. Included in this figure are experiments with and without lipid. In all these experiments, total dissolved iron is used as the progress variable, which is appropriate for these conditions because the concentration of both ferrous and ferric iron is not limited by the precipitation of an iron oxide at the low solution pH maintained in these experiments [23].

There are at least three important observations that can be made. First, the rate of oxidation is the highest for experiments in which pyrite without a lipid pretreatment is exposed to A. ferrooxidans. Second, if the pyrite is exposed to lipid, prior to the exposure to the bacteria, there is a significant decrease in the amount of pyrite oxidation. Specifically, over the last 10-day period (where the solution is supporting the steady growth of the bacteria; see below) of the experiment, there is a >4-fold decrease in the oxidation rate when pyrite has an adsorbed lipid layer. Third, while lipid suppresses the amount of bacterial-induced pyrite oxidation, the rate of oxidation in the presence of microbes is higher than in the absence of microbes. Hence, the presence of the lipid on the pyrite surface does not entirely suppress the influence of the bacteria. For example, over the last 10-day period, the amount of oxidation associated with the bacteria/lipid/pyrite system was a factor of three higher than the rate of oxidation associated with the abiotic lipid/pyrite system, and it was very similar (within experimental error) to the rate of oxidation associated with untreated pyrite in pH 2 water (i.e., no bacteria or lipid).

A summary of these data, including the amount of suppression exhibited by the lipid coating over the last 10 days of each experimental run in the biotic and abiotic environments are given in Table 1. The rates measured in this study of 2.1 × 10-9 and 1.62 × 10-8 mol/m2-s at pH 2 for the abiotic and biotic circumstance, respectively, are in reasonable agreement with prior studies that investigated the oxidation of pyrite in the presence of A. ferrooxidans. Differences in pH, cell density, mineral surface area, and growth media between studies all lead to variability in the measured abiotic and biotic rates. Prior research by Olson, for example, measured abiotic and biotic oxidation rates of ~2 × 10-9 and ~9 × 10-8 mol/m2-s, respectively at a pH close to 2, [24] while a recent study at a similar pH measured the biotic rate to be 7 × 10-10 mol/m2-s [13]. We emphasize that while our measured rate fall within the spread associated with prior studies, perhaps more important to this study is that the rate of pyrite oxidation in the presence of bacteria can be significantly suppressed when phosphochloine lipid is adsorbed on pyrite (a rate decrease from 1.62 × 10-8 to 3.1 × 10-9 mol/m2-s).

Table 1. Summary of experimental observations for the amount of pyrite oxidation in the presence of lipid and bacteria.

In order to understand the role of bacteria in promoting pyrite oxidation in systems treated with lipids it is useful to analyze the distribution of bacteria between the mineral and the solution phase. As a first step toward this analysis it is necessary to confirm that cells measured by microscopy as being bound to the surface are in fact truly mineral-bound and not a superficial bacterial layer that results from the preparation of the samples. Epifluorescence images of the bacterial/pyrite samples illustrate these differences in bacterial attachment (Figure 2). Images 2a and 2b compare the bacteria/pyrite and bacteria/lipid/pyrite samples, respectively, after the samples were exposed to oxidizing conditions in solution for 10 days. The pyrite particles are not visible with epifluorescence microscopy (because the fluorochrome dyes used for staining cells specifically bind to protein and/or DNA only), and bacteria that are attached to the pyrite are visible as microcolonies (cell aggregates). This observation is common when visualizing surface-bound cells on organic or inorganic particles by epifluorescence microscopy. Such microcolonies of surface-bound bacteria were abundant in the pyrite/bacteria sample (Image 2a) but not the pyrite/lipid/bacteria sample (Image 2b) (quantification of images to determine cell densities was also performed and is presented below.) These images suggest that the presence of the lipid impedes the interaction of the bacteria with the pyrite surface. To support our contention that the bacteria are actually bound to the pyrite particles, the samples were vigorously vortexed prior to imaging (see Figure 2c and 2d). After this treatment, the bacterial aggregates were still present, suggesting a strong ad