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Applied and Environmental Microbiology, December 1999, p. 5474-5483, Vol. 65, No. 12
University of Puget Sound, Tacoma, Washington
98416
Received 14 May 1999/Accepted 15 September 1999
At Chocolate Pots Hot Springs in Yellowstone National Park the
source waters have a pH near neutral, contain high concentrations of
reduced iron, and lack sulfide. An iron formation that is associated with cyanobacterial mats is actively deposited. The uptake of [14C]bicarbonate was used to assess the impact of ferrous
iron on photosynthesis in this environment. Photoautotrophy in some of the mats was stimulated by ferrous iron (1.0 mM). Microelectrodes were
used to determine the impact of photosynthetic activity on the oxygen
content and the pH in the mat and sediment microenvironments. Photosynthesis increased the oxygen concentration to 200% of air saturation levels in the top millimeter of the mats. The oxygen concentration decreased with depth and in the dark. Light-dependent increases in pH were observed. The penetration of light in the mats and
in the sediments was determined. Visible radiation was rapidly
attenuated in the top 2 mm of the iron-rich mats. Near-infrared radiation penetrated deeper. Iron was totally oxidized in the top few
millimeters, but reduced iron was detected at greater depths. By
increasing the pH and the oxygen concentration in the surface
sediments, the cyanobacteria could potentially increase the rate of
iron oxidation in situ. This high-iron-content hot spring provides a
suitable model for studying the interactions of microbial
photosynthesis and iron deposition and the role of photosynthesis in
microbial iron cycling. This model may help clarify the potential role
of photosynthesis in the deposition of Precambrian banded iron formations.
Phototrophic mats at Chocolate Pots
Hot Springs in Yellowstone National Park form an important boundary
layer at the interface of the iron sediment surface and the flowing
spring water, which contains about 100 µM ferrous iron at the source
(55). We analyzed the structure of these mats and identified
four different types of mats composed predominantly of cyanobacteria,
although the anoxygenic phototroph Chloroflexus sp. appeared
to be an important constituent of the mats at the highest temperature
(55). The major pigments in most of the mats are chlorophyll
a, phycocyanin, and carotenoids. Bacteriochlorophyll
a is present in some sediments, and both bacteriochlorophyll
a and bacteriochlorophyll c are present in
Synechococcus mats that contain Chloroflexus sp.
(55). A colorful iron formation is being deposited at these
hot springs (1). The microbial mats, which are composed
chiefly of filamentous gliding phototrophs, may play a substantial role
in stabilizing oxidized iron, thereby enhancing accumulation of soft
sediments that can be compacted to form the iron deposits
(55).
The evolution of photosynthesis in the Precambrian is tightly linked to
major changes in the oxidation states of the atmosphere, hydrosphere,
and lithosphere. The increase in the atmospheric oxygen content around
2,000 million years ago was probably due to the widespread development
of oxygenic photosynthetic cyanobacteria (33, 60).
Production of oxygen as a photosynthetic waste product resulting from
the oxidation of water is a physiological capability that must have
arisen in the cyanobacterial ancestors much earlier than this and
perhaps occurred as early as 3,500 million years ago (60).
Ancient Archean banded iron formations (BIFs) containing various
amounts of oxidized iron have been used as evidence that early
localized production of oxygen by cyanobacterial photosynthesis occurred (7, 8, 10).
Other workers have proposed that the activity of anoxygenic phototrophs
capable of directly oxidizing ferrous iron may account for the
relatively low levels of oxidized iron in BIFs without invoking the
presence of oxygen (19, 20, 30, 36, 47, 50, 53, 66, 68).
Cohen has suggested (12, 13) that cyanobacteria may also be
capable of directly oxidizing iron without producing oxygen. Pierson
and Olson (50) have postulated that iron-dependent
photosynthesis may have been an important step in the evolution of
oxygenic photosynthesis in ancestral cyanobacteria. The various redox
potentials of reduced iron which are influenced by environmental pH and
the presence of complexing ions (15, 25) make reduced iron a
potential electron donor for photosystem I (PSI) and PSII types of
reaction centers (RC1 and RC2, respectively). The widespread abundance
of reduced iron on the early Earth prior to the appearance of oxygen
would have made it particularly suitable as an electron donor for
photosynthesis. Pierson et al. (52) have also pointed out
that the oxidized iron products of this type of photosynthesis could
have provided substantial protection from UV radiation for
surface-dwelling phototrophs prior to the development of an ozone shield.
Chocolate Pots Hot Springs is a hydrothermal system in which we are
investigating the interaction of phototrophs with reduced and oxidized
iron in a setting in which an iron formation is actively being
deposited. While it is not representative of the deep-ocean models of
Precambrian iron deposition (34), the Chocolate Pots iron
formation provides a suitable system in which to study the potential
impact of photosynthesis on iron oxidation and mineralization processes
and to explore hypotheses regarding the association of phototrophic
prokaryotes with iron. The association of well-developed contemporary
microbial mats with an iron-depositing environment is a model that has
been missing for the microfossiliferous stromatolites of the Gunflint
Iron Formation (9, 10, 35). Chocolate Pots Hot Springs
provides such a model.
At first, a shallow subaerial hot spring in a contemporary oxic
atmosphere may not seem to be a suitable model for studying the
mechanisms of iron oxidation in the anoxic Precambrian world. One might
suppose that all of the reduced iron in the source waters is
immediately oxidized by the abundant oxygen in the atmosphere, leaving
a ferrous iron-depleted system in which to try to study microbial
processes. Chemical oxidation rates are relatively low compared to
enzymatically based metabolism, however, (21, 22, 31, 32),
and such rates are greatly influenced by other factors, such as pH
(25, 26, 37). The water flows quickly down steep slopes at
Chocolate Pots, and much reduced iron is still in solution at the base
of the thermal gradient (see Table 1). Water also flows through
microchannels or interstitial voids within biofilms, not just
over the surface (38). It is known that even in very active
oxygenic cyanobacterial mats the oxygen is depleted within a few
millimeters or less of the surface (6, 17, 57, 58, 64).
Furthermore, in the absence of oxygen, anaerobic microbial activity can
reduce Fe(III) to Fe(II) (18, 39, 44, 45, 59, 65).
Consequently, just beneath the surface of the microbial mat-water
interface, the environment can be quite different, anoxic, and rich in
Fe(II). The processes that occur in this area may well represent
processes that occurred on a more extensive scale in an ancient anoxic world.
In a related study we characterized the specific phototrophs, the mat
structure, and the physical associations of the organisms with the
accumulating iron deposit (55). We found that filamentous phototrophs are intimately associated with the iron mineral grains and
that the motility and orientation of the filaments may be important for
trapping and stabilizing the sediments to produce the iron formation.
We found that these characteristics are most evident in an olive mat
consisting of a narrow Oscillatoria sp., which is the major
mat that dominates the iron formation studied (55). Mats
dominated by Oscillatoria cf. princeps are much
more limited in distribution. At the highest hot spring temperatures (50 to 54°C) the mats were composed primarily of
Pseudanabaena sp. in some places and of
Synechococcus and Chloroflexus spp. in other places.
In this study, our overall objective was to assess the potential impact
of microbial photosynthesis on the deposition of an iron formation. We
investigated the photosynthetic activity in microbial mats by using
microelectrodes in order to measure the potential impact of this
activity on oxygen and pH, which can influence iron transformations in
mats. We also investigated the impact of iron on the physiology of
photosynthesis and the impact of iron deposition on the availability of
light in the photosynthetic microenvironment. Although we conducted
experiments with all four types of photosynthetic mats present, as well
as with non-mat-covered sediments at Chocolate Pots, our emphasis was
on the most pervasive olive cyanobacterial mat.
Microelectrode studies.
Microelectrode profiles were
determined in situ and with excised mat samples. Because of the steep
and rocky nature of the site, it was very difficult to obtain the in
situ profiles. Therefore, most of the profiles were determined with
excised mat samples within 5 h of collection from the hot spring.
Mat samples were maintained at the in situ temperatures in a water bath
while electrode profiles were obtained. The entire apparatus was placed
under a grounded Faraday cage in order to reduce electrical noise and to regulate the light intensity. The average light intensity under the
cage for most profiles was 600 to 700 W m
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Phototrophs in High-Iron-Concentration Microbial Mats:
Physiological Ecology of Phototrophs in an Iron-Depositing Hot
Spring
ABSTRACT
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
INTRODUCTION
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
MATERIALS AND METHODS
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
2.
Neutral-density screens were placed on the Faraday cage in order to
reduce the light intensity when necessary. Dark conditions were
produced by draping black cloths over the cage. The irradiance in the
darkened cage was 0 to 4 W m2. Mats were preincubated in
spring water in the light or in the dark for 1 to 2 h at the in
situ temperatures before electrode measurements were obtained. All
profiles were completed in 20 min. Most mat samples were 2 to 4 mm
thick. The thinner mats were supported on an agar base when their
profiles were obtained. Light intensities were measured with a
pyranometer sensor (model LI-185B; LI-COR, Lincoln, Nebr.), and
temperatures within the mats were measured with a model 52 K/J
thermometer and bead probe (Fluke, Everett, Wash.).
0.75 V. Current was measured
with an autoranging picoammeter (model 485; Keithly, Cleveland,
Ohio). Air saturation values for oxygen were determined by using
compressed air to saturate spring water at the recording temperature.
Zero oxygen was measured by using zero pO2 ampoules (type
S4150; Radiometer, Copenhagen, Denmark).
Water chemistry. The concentration of Fe(II) in the spring water was measured by the ferrozine assay (21, 62). A 0.01-ml sample removed directly from the spring was immediately added to 2.49 ml of a ferrozine solution (0.01% ferrozine in 50 mM HEPES) (Sigma Chemical Co. St. Louis, Mo.), and the preparation was mixed and returned to the lab, where the absorbance at 562 nm was read within 2 h.
Oxygen levels in the flowing water were measured by using a model 51B oxygen meter and a model 5739 probe (Yellow Springs Instrument Co., Yellow Springs, Ohio) with direct temperature, altitude, and salinity compensation. The pH was measured by using ColorpHast pH papers 4.0-7.0 and 6.5-10.0 (EM Science, Gibbstown, N.J.) and a pH meter and probe (model 6009; Jenco, San Diego, Calif.). Temperatures were measured with the model 52 K/J thermometer and a bead probe (Fluke).14C uptake experiments. All [14C]bicarbonate uptake experiments were performed in the lab by using excised mats as previously described (54). The mats were examined microscopically to ensure that one type of cyanobacterium was dominant, and an even cell suspension was prepared by using a glass tissue homogenizer and source water. 14C-labeled NaHCO3 was added to a final concentration of 0.2 µCi/ml. DCMU was added to a final concentration of 5 µM when necessary. A stock solution of ferrous chloride was prepared and added anoxically to final concentrations of 0.5, 1.0, 2.5, 5, 10, 25, and 50 mM. All solutions and vials were sparged with argon to prevent oxidation of Fe(II). All preparations were incubated in 2-ml vials filled to the neck.
The vials were incubated horizontally to maximize light exposure in petri dishes blackened on the sides and bottoms, and layers of neutral-density screen were used to vary the light intensity as described previously (54). Dark controls were incubated in totally blackened dishes. Samples were incubated in a water bath at the temperature of the original mat. For most experiments the light intensity was 150 to 300 W m2. Photosynthesis was stopped
by adding 0.1 ml of formalin, the samples were filtered onto membrane
filters (diameter, 25 mm; pore size, 0.45 µm; Gelman Metricel, Ann
Arbor, Mich.), and the radioactivity was counted by using Ultima Gold
LSC cocktail (Packard, Meriden, Conn.) as previously described
(54).
Spectral irradiance. Light penetration through the microbial mats was measured with a model LI-1800 spectroradiometer (LI-COR) by layering the mats on a remote cosine receptor (model 1800-11) (51). All measurements were made in June and July in full sun at an elevation of 2,100 m.
Quantitative pigment analysis. Chlorophyll concentrations in the suspensions during the 14C uptake studies were measured as previously described (49, 54, 55). Spectra were recorded with a model UV-1601 spectrophotometer (Shimadzu, Columbia, Md.).
Iron distribution in mats. Ferrous iron contents were measured by using the ferrozine assay. Total iron contents were determined by reducing samples with 0.25 M hydroxylamine in 0.25 M HCl before ferrous iron contents were measured by the ferrozine assay as described previously (21, 62). The ferric iron content was calculated by subtracting the ferrous iron content from the total iron content.
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RESULTS |
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Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
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Impact of cyanobacteria on water chemistry.
Measurements were
obtained at the following three sites along the hot spring outflow: the
source, midway down the channel (about 7 m from the source), and
at the end of the drainway where the spring flowed into a river (about
15 m from the source). The concentration of Fe(II) in the water in
the main drainway of the hot spring decreased from the source down the
outflow channel, while the concentration of oxygen in the water and the
pH increased (Table 1). The oxygen
content reached saturation values before the drainway ended, but
considerable Fe(II) still remained in solution. Measurements obtained
in the early morning were compared with measurements obtained late in
the afternoon. We observed few changes in the oxygen and Fe(II)
contents of the flowing water that could be attributed to the
biological activity of the mat phototrophs (Table 1). The pH downstream
from the source was higher in the late afternoon than in the early
morning.
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Impact of cyanobacterial photosynthesis on the iron sediment microenvironment. The cyanobacteria in Chocolate Pots Hot Springs formed conspicuous green mats among the iron sediments. The surface millimeter of the mats contained the densest accumulations of cyanobacteria, which were closely associated with granules of iron oxides. Beneath the surface layer, the number of phototrophs decreased, and conspicuous orange iron oxide deposits were present. The sediments were often sufficiently consolidated by the microbial masses to form a cohesive layered mat several millimeters thick (55).
When we assessed the potential impact of the phototrophs on the oxygen levels in the sediment environment by using needle-encased microelectrodes, we found that photosynthetic activity substantially altered the prevailing conditions in the sediments. During four field seasons (1995 through 1998) we obtained more than 100 depth profiles for oxygen and pH by using more than 50 excised or in situ mat and sediment samples. Although lateral heterogeneity was observed within mats and there were variations among the different types of mats and sediments, the depth profiles were fundamentally similar and maximum oxygen contents usually occurred in the top millimeter (Fig. 1A through C).
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2) were much higher than the light intensities under the
Faraday cage (700 W m2), and these higher light
intensities resulted in photoinhibition near the surface of the mat.
After complete profiles were obtained, the electrode was positioned at
a fixed depth of 0.25 mm in the mat (Fig. 1C). When the surface light
intensity was 910 W m2, the oxygen concentration was 161 µM. When the surface light intensity was decreased to 540 W
m2, the oxygen concentration increased to 202 µM.
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2 at the surface) and then exposed to
decreasing light intensities over a 20-min period. It then remained in
the dark for 10 min and was subsequently exposed to increasing light
intensities for another 20 min. Changes in the oxygen levels were
detected within seconds of each change in light intensity (Fig. 3). The
oxygen concentrations leveled out and stabilized within minutes of each shift. Similar, although less dramatic, changes were observed for pH
levels in response to changes in light intensity (data not shown).
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2 at the mat surface), and the oxygen
concentration was 238 µM (155% of saturation) under these
conditions. When the light intensity at the surface was suddenly
decreased to 140 W m2, the oxygen concentration decreased
to 201 µM in 10 s and to 181 µM in less than 1 min. When the
light intensity was returned to 1,100 W m2, the oxygen
concentration rose to 228 µM in less than 30 s.
Impact of iron on cyanobacterial photosynthesis. The impact of ferrous iron on photosynthesis in the cyanobacterial mat populations was assessed by measuring the fixation of 14C-labeled bicarbonate under different conditions. Uptake experiments were performed with dilute suspensions of the mat communities incubated under moderate to low light intensities to avoid photoinhibition.
Both in the light and in the dark, ferrous iron stimulated bicarbonate uptake in the olive mat, and maximal stimulation occurred at a concentration of 1.0 mM (Fig. 4A). Ferrous iron at a concentration of 5 mM inhibited photosynthesis (although not uptake in the dark), and higher concentrations of iron eliminated photosynthetic activity and depressed activity in the dark (Fig. 4A). The iron enhancement of dark-corrected uptake in the light was substantial in this experiment, and the levels were as high as 175% of the non-iron-containing control levels. In other experiments, however, the stimulation was much less substantial and perhaps not significant (Fig. 4B). No evidence of inhibition of photosynthesis by 1.0 mM ferrous iron was ever observed in the olive mat, although this concentration of ferrous iron did inhibit Oscillatoria cf. princeps mat suspensions (data not shown). Photosynthesis in Pseudanabaena spp. was not consistently stimulated by ferrous iron (1.0 mM) (data not shown). Ferrous iron (1.0 mM) strongly stimulated light-dependent uptake of bicarbonate (500% of the no-iron control value) but not uptake of bicarbonate by the Synechococcus mat suspensions in the dark (Fig. 5). A high level of stimulation was observed consistently in four different experiments with Synechococcus mat suspensions. DCMU inhibited photosynthetic activity both in the presence and in the absence of iron in all mat suspensions (Fig. 4B and 5). In all of the mat suspensions, 10 mM ferrous iron strongly inhibited uptake both in the light and in the dark (Fig. 4 and 5).
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Nature of the light environment in mats and in iron sediments. The downward spectral irradiance penetrating the top 1 mm of packed iron sediments devoid of cyanobacterial mats lacked specific pigment absorption signatures (Fig. 6B). The sediments transmitted relatively little visible radiation (wavelengths, 400 to 700 nm) due to attenuation from scattering and absorption by the iron minerals (Fig. 6B). However, they transmitted considerable red and near-infrared (NIR) radiation and retained most of the solar spectral characteristics at the NIR wavelengths (700 to 900 nm) (Fig. 6A and B).
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Iron distribution with depth.
The concentrations of ferrous
iron increased and the concentrations of ferric iron decreased in the
mat sediments as the depth increased (Fig.
7). The total iron concentration remained
constant at around 50 µg mm of wet sediment3.
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DISCUSSION |
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Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
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We observed novel stimulation of photosynthetic bicarbonate uptake by Fe(II) in suspensions of phototrophic mats obtained from Chocolate Pots Hot Springs and analyzed the microbial ecology of cyanobacterial mats in this high-iron-concentration thermal environment. The iron stimulation of photosynthesis which we observed is particularly interesting and is discussed below, as is our interpretation of the ecological data and its potential relevance to the microbial geochemistry of iron formations.
Impact of iron on photosynthesis in cyanobacterial mats. Iron [Fe(II)] stimulated [14C]bicarbonate uptake in the olive mat, and it did so most consistently in the Synechococcus mat suspensions. In the olive mat suspensions, the maximal dark-corrected stimulation of photosynthesis which we observed was 175% of the control value, which occurred in the presence of 1.0 mM Fe(II). In Synechococcus mat suspensions, the stimulation was very consistent and considerably greater than the stimulation in olive mat suspensions; the values were as high as 500 to 600% of the control values. There are three reasonable explanations for the stimulation of photosynthesis observed in the presence of iron. One hypothesis is that the Fe(II) increases the photosynthetic rate by lowering the redox potential or reducing the amount of free oxygen that builds up during oxygenic photosynthesis, which can potentially become inhibitory (43, 48, 67). However, when we tested an alternative reductant (thioglycolate), which was used by Weller et al. (67) to lower the redox potentials in suspensions of hot spring cyanobacteria, stimulation of photosynthesis was not observed (data not shown).
The second hypothesis is that Fe(II) functions as an electron donor during cyanobacterial photosynthesis in some of the Chocolate Pots mats. Some mat-forming cyanobacteria, such as marine Microcoleus spp. and some Oscillatoria species from hot springs (11), are known to use sulfide to sustain anoxygenic photosynthesis. The magnitude of the iron stimulation of photosynthesis which we observed in the olive mat suspensions was comparable to the magnitude reported for sulfide stimulation in cyanobacteria (11). The iron stimulation which we observed in the Synechococcus mat suspensions was greater than the sulfide stimulation observed in cyanobacterial cultures (11). Iron actually inhibited photosynthesis in the Oscillatoria cf. princeps mat suspensions, however. Cohen et al. (11) likewise showed that although sulfide stimulated photosynthesis in some cyanobacteria, it strongly inhibited photosynthesis in others. Although we have not eliminated the possibility that iron stimulates photosynthesis in some cyanobacteria by lowering the redox potential or consuming oxygen, our data suggest that iron may directly support photosynthesis in some of these organisms; these findings are similar to the sulfide findings of Cohen et al. (11). Cohen explored the possibility that Fe(II) is an electron donor for cyanobacterial photosynthesis and found evidence which supported this possibility (12, 13). It is not clear from Cohen's early findings whether cyanobacteria use iron as an electron donor for PSI or PSII (12, 13). Sulfide appears to donate electrons exclusively to PSI in cyanobacteria. However, both sulfide and Fe(II) can donate electrons to PSII-related RC2 reaction centers in purple bacteria (19, 20, 68). Therefore, it seems at least plausible that Fe(II) can donate electrons to cyanobacterial PSII. The lower pH values of source waters in which Synechococcus-Chloroflexus mats are found could increase the redox potential of the Fe(III)-Fe(II) couple, bringing it closer to the potential of the PSII reaction center chlorophyll a (P680). It is not unreasonable to postulate that such a mechanism was part of an evolutionary process leading to water-oxidizing PSII in cyanobacteria (47, 50). The third hypothesis is that Fe(II) stimulates photosynthesis in anoxygenic phototrophs present in some of the cyanobacterial mat suspensions rather than in the cyanobacteria themselves. These putative photoferrotrophs could use mechanisms of photosynthetic iron oxidation similar to mechanisms used by the iron-dependent purple bacteria recently described by Ehrenreich and Widdel (19, 20) and Widdel et al. (68). The Synechococcus mat which exhibited the highest level of iron stimulation also contained abundant Chloroflexus filaments. Members of the genus Chloroflexus contain bacteriochlorophylls and a reaction center similar to that of the purple bacteria, so it is possible that some Chloroflexus strains may indeed be able to oxidize Fe(II) to support photoautotrophy. Thermophilic mat-forming Chloroflexus strains have been shown to use sulfide for photosynthetic CO2 fixation in hot springs in the Mammoth area of Yellowstone National Park (27). The DCMU data set some limits on the possible ways to explain iron stimulation of photosynthesis. Cohen et al. (11) showed that sulfide-dependent anoxygenic photosynthesis in cyanobacteria was not sensitive to DCMU and therefore was a function of PSI. In our experiments performed with iron, all photosynthetic activity [with and without Fe(II)] was inhibited by DCMU. This observation suggests that direct reduction of the reaction center in PSI (which is not sensitive to DCMU) by Fe(II) does not occur in the cyanobacteria examined. Our results are consistent with the interpretation that if Fe(II) donates electrons for photosynthesis in some of these cyanobacteria, it donates them to a PSII type of reaction center, as suggested by Cohen et al. (11). Cyanobacteria with this iron-oxidizing ability would not necessarily be distributed widely. They would exist only in environments such as Chocolate Pots Hot Springs, which contain abundant Fe(II) that is not consumed immediately by iron-oxidizing chemotrophs or directly by oxygen. The Fe(II) might inhibit water-oxidizing activity and then be an electron donor in the same RC2 reaction center, or it might donate electrons to another RC2-like reaction center specialized for iron oxidation in order to augment CO2 fixation. Generally, Chloroflexus strains containing a PSII type of reaction center (RC2) have been shown to be photosynthetically insensitive to DCMU (3, 67). It is possible, however, that an anoxygenic RC2 reaction center capable of oxidizing iron would be sensitive to DCMU. Apparently, it is not known yet whether the iron-oxidizing photosynthetic purple bacteria are sensitive to DCMU (19, 20, 68). Isolation of the Chocolate Pots mat phototrophs and experiments performed with pure cultures are needed to distinguish among the proposed novel physiological activities.Impact of cyanobacterial mats on water chemistry. The ferrous iron and oxygen contents of the spring water flowing over the mats changed little between early morning and late afternoon, and based on this information we concluded that cyanobacterial photosynthetic activity had little impact on either parameter. The springs were shallow; the oxygen concentrations in the flowing water reached near air-saturated levels quickly, and the water was never supersaturated. Consequently, the major source of oxygen in the flowing spring water was mixing with air rather than photosynthesis in the mats below.
It was assumed that most of the iron in the water flowing over the mats was oxidized by the air-saturated water. Some of the resulting oxidized ferric precipitates settled out in quieter areas on the mound, while the finer precipitates were carried into the river by the rapidly flowing water. Although the Fe(II) levels in the water decreased down the drainway as the oxygen content increased, Fe(II) was still detected where the effluent flowed into the river. High rates of photosynthesis in the mats may have contributed to the increase in pH in water downstream from the source. This increase was substantially higher in the late afternoon than in the early morning. Revsbech and Ward (57) observed that in Octopus Spring mats and in the overlying water the highest pH occurred in late afternoon. The Chocolate Pots spring waters appeared to be affected similarly.Impact of cyanobacterial mats on the chemistry of the sediment environments. In contrast to the flowing water, the microenvironment consisting of the mat-containing sediments was affected substantially by the photosynthetic activity of the cyanobacterial mats. Several experiments confirmed that cyanobacterial photosynthesis played a role in oxygenating the sediments. (i) Microelectrode depth profiles revealed that the oxygen levels in the mats in the light exceeded the air saturation levels characteristic of the flowing water by more than 200%, while the values in the dark never exceeded the air saturation levels and were often much less. (ii) In the places where sediments were devoid of cyanobacterial mats, the oxygen concentration was not elevated in the light, and the values never exceeded the values obtained from air saturation alone. (iii) The oxygen concentrations in the mats changed rapidly in response to changes in light intensity, as observed by Revsbech and Ward (57) for Octopus Spring mats. (iv) DCMU reduced the oxygen levels in mats by shutting down PSII. (v) The in situ oxygen profiles showed that local cyanobacterial oxygen production rather than the aerated flowing spring water was the critical factor in determining oxygenation of sediments. When the area being measured with the electrode was darkened, the oxygen levels decreased steeply despite the fact that photosynthesis was still occurring in mats located immediately upstream from the electrode.
The depth profiles for oxygen and pH in the light and in the dark in the Chocolate Pots cyanobacterial mats were typical of the profiles obtained for other cyanobacterial mats, including thermal mats in hot springs in which the concentration of iron is low (57, 58). As observed by Revsbech and Ward (57, 58), we found that the changes in pH value were not always as dramatic or as consistent as the changes in oxygen concentration. The actual concentrations of oxygen in the Chocolate Pots mats in the light, although well above the air saturation values, were still considerably lower than the concentrations observed in low-iron-concentration thermal springs (57, 58). The continuous supply of reduced iron in the Chocolate Pots source water could have consumed some of the oxygen. All of the microelectrode profiles and in situ observations discussed above demonstrated that cyanobacteria create a microenvironment in which it is possible that the rate of oxidation of Fe(II) increases to a value that is greater than the value possible with air exposure alone. Water flows through the microchannels and interstitial voids of mats and biofilms, which enhances the direct interaction of microbes with water chemistry (16, 38). The pore water is clearly affected on a diel basis by the photosynthetic activity of the cyanobacteria and perhaps by the chemotrophic activity of other autotrophs and heterotrophs. Our data confirmed that in the light both the pH and the oxygen concentration of the pore water of mat-dominated sediments are significantly higher than the pH and the oxygen concentration of the flowing spring water above the mat, and thus the rate of oxidation of reduced iron may be increased. Since the microenvironment of the mats becomes anoxic in the dark, Chocolate Pots Hot Springs should provide an excellent model with which to directly test the impact of photosynthesis on iron oxidation and mineralization in situ.Comparison of Chocolate Pots cyanobacterial mats to other iron-containing systems. Emerson and Revsbech (21) studied oxygen profiles in the sediments of a cold iron-containing spring that was devoid of cyanobacteria and was dominated by chemotrophic iron bacteria. The oxygen concentrations in the depth profiles which these authors obtained never exceeded the ambient air saturation values. The oxygen concentrations decreased sharply with depth primarily due to respiratory consumption by chemotrophs in the mats containing iron bacteria (22). In contrast, we did not observe rapid depletion of oxygen with depth in plain sediments that lacked cyanobacterial mats (Fig. 1D), which indicated that similar purely chemotrophic iron-oxidizing mats were probably not present in the Chocolate Pots springs.
However, in many sediments containing cyanobacterial mats, we did observe rapid and strong depletion of oxygen with depth in the light and greater depletion in the dark; most mats became anoxic. We attributed this oxygen depletion in the mat-dominated sediments at Chocolate Pots to metabolic consumption. Respiratory activity can occur in phototrophs, as well as in chemoautotrophs and chemoheterotrophs. The fact that oxygen depletion did not occur in the sediments that lacked mats is evidence that purely chemical oxidation of reduced iron is not the major factor that contributes to oxygen depletion in the mats. Thus, we concluded that microbial metabolism in well-developed mats is the major cause of oxygen depletion; Emerson and Revsbech (21, 22) reached a similar conclusion concerning their purely chemotrophic iron mats. The pH values which we obtained (pH 8 to 9) were much higher than the values reported by Emerson and Revsbech (21) (pH 7.1 to 7.6), probably because of the high rates of autotrophic activity in the photosynthetic mats which we studied. We observed some lower pH values closer to neutral in the dark or deeper in some mats and sediments. Interpretation of changes in pH, however, may be complicated by the presence of other organisms (46) and the effects of abiotic water chemistry. In one sediment sample that lacked a cyanobacterial mat, we observed a light-dependent increase in pH without an accompanying increase in the oxygen concentration at depths of 0.25 to 1.25 mm (Fig. 1D). Since NIR radiation penetrates to this depth (Fig. 6B), this increase in pH could indicate that anoxygenic photoautotrophs were present.Light penetration in Chocolate Pots Hot Springs mats and sediments. The presence of oxidized iron minerals in mats and sediments affects the light environment by selectively attenuating short-wavelength visible radiation and transmitting red and NIR radiation. The dominant phototrophs in the mats are cyanobacteria, which also selectively attenuate visible radiation. NIR radiation penetrated below the cyanobacterial layers to depths greater than 2 mm and provided a light environment that could support bacteriochlorophyll-containing anoxygenic phototrophic bacteria. If iron-dependent photoautotrophs, such as those described by Ehrenreich and Widdel (19, 20), were present, they could contribute to direct oxidation of Fe(II) and thus enhance iron mineralization in the sediments. Fe(II)-containing enrichment cultures obtained from some of the sediments have revealed that purple bacteria are present (unpublished data). Although purple photosynthetic bacteria are present in the springs, the distribution and abundance of these organisms are more limited than the distribution and abundance of cyanobacteria. The one mat containing substantial bacteriochlorophyll was the Synechococcus mat which contained Chloroflexus filaments, as in other hot springs in the region (55).
Iron reduction and cycling. Although we studied only photosynthetic activity in the mats, depth profiles for Fe(II) and Fe(III) (Fig. 7) showed that the Fe(II) fraction of the total iron started to increase with depth at 2 mm. This increase coincided with the depth of anoxia in both the light and the dark in most mat-dominated sediments (but not in plain sediments). Our data suggest that too little short-wavelength light reaches this depth (Fig. 6) to sustain abiotic photoreduction of iron (14, 24, 40, 41). The increase in the Fe(II) concentration with depth, which was accompanied by a corresponding decrease in the Fe(III) concentration, could be evidence that the microbes present exhibited iron-reducing activity. It would not be surprising to observe microbial iron reduction below the oxic zone of the mats since cyanobacteria produce abundant organic substrates that could be sources of carbon and reducing power. Iron-reducing bacteria have been detected in many types of sediments (39, 45).
Chocolate Pots Hot Springs mats provide a unique high-iron-concentration environment in which to study the cycling of iron among iron oxidizers, reducers, and phototrophs. The presence of a rapidly flowing shallow water zone that appears to be primarily abiotic, a 2-mm-thick phototrophic mat in which there are diel shifts in oxic and anoxic conditions, and a permanently anoxic zone that may receive small amounts or NIR radiation provides a compact environment that is less than 1 cm deep in which to study aerobic and anaerobic biotic and abiotic transformations of iron.Geochemical significance and BIFs. The geochemical potential of microbial iron transformation was noted in the early studies of chemotrophic iron bacteria (29, 56, 71). There has been speculation about the role of bacterial oxidizing activities in the deposition of the Precambrian BIFs (31, 32), including the role of photosynthesis (7, 36, 66, 68). Although many models for the deposition of iron formations have been proposed, most researchers favor the stratified deep-ocean model; according to this model high concentrations of ferrous iron and silica accumulated in deep anoxic water and precipitated when the anoxic water was mixed with more oxic water from above, and biological activity was not required (4, 34).
Recent studies performed in natural aquatic systems have shown that oxidation of Fe(II) to Fe(III) can proceed by a variety of mechanisms. The rate is influenced by a large number of factors, including pH, the presence of surfaces, the concentration of oxygen, the presence of other oxidants, and biological activity. Photochemically produced hydrogen peroxide can be a significant factor (42, 69, 70). Biological activity has been found to accelerate the rate of iron oxidation in mildly acidic freshwater lake sediments (2) and in a shallow water marine hydrothermal environment (31, 32). Holm (31, 32) favored Simonson's hydrothermal model (61) for the origin of BIFs but suggested that the low levels of oxygen required could have been provided by early cyanobacteria, as proposed by Cloud (7). Microaerophilic chemolithotrophs could have enhanced the rate of iron oxidation, as suggested by Emerson and Revsbech (21, 22), Emerson and Moyer (23), and Holm (31, 32). Anaerobic oxidation of iron is also possible (28, 63). Whether phototrophs play a direct or indirect role or no role in the oxidation of iron in natural environments has not been determined yet.Conclusions. We confirmed that microbial photosynthetic activity has a significant impact on the sedimentary microenvironments in a high-iron-concentration thermal spring. We are currently determining the quantitative impact in real time of photosynthetic microbial activity on the rates of oxidation of iron and the subsequent early mineralization of iron in microbial mat sediments. We have detected iron-dependent stimulation of photosynthesis in some mats and are currently trying to identify the nature of this stimulation.
While deep-sea hydrothermal effluents can obviously be factors that contribute to the deep-ocean model of BIFs, subaerial hot springs cannot. Nevertheless, studies of the iron being deposited at Chocolate Pots Hot Springs provide a unique opportunity to test some of the hypotheses regarding the role of biological activity in iron oxidation and deposition in which the primary source of ferrous iron, silica, and carbonate is a hydrothermal fluid. In this setting, the oxygenic photosynthetic cyanobacteria substantially increase the oxygen concentration and pH compared to the ambient environmental conditions. Thus, Chocolate Pots Hot Springs provides an accessible subaerial iron model in which biogenic effects on reduced iron can be studied. Furthermore, the complex microbial community that could develop at this site within and beneath the steep, fluctuating oxygen and light gradients provides a unique opportunity to study a wide range of direct and indirect microbial interactions during the cycling of iron.| |
ACKNOWLEDGMENTS |
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This work was supported by grant NAGW-5090 from the NASA Exobiology Program to B.K.P. During 1997, B.K.P. was supported by a John Lantz Senior Research Fellowship from the University of Puget Sound. Research funds were also provided by the University of Puget Sound Enrichment Committee.
We thank R. W. Castenholz for helpful comments. We thank the National Park Service for permission to conduct research in Yellowstone National Park.
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FOOTNOTES |
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* Corresponding author. Mailing address: Biology Department, University of Puget Sound, 1500 N. Warner, Tacoma, WA 98416. Phone: (253) 756-3353. Fax: (253) 756-3352. E-mail: bpierson{at}ups.edu.
Present address: Center for Microbial Ecology, Michigan State
University, East Lansing, MI 48824.
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REFERENCES |
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Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
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