Impact Factor 5.640 | CiteScore 7.3
More on impact ›


Front. Microbiol., 03 March 2022 |

Biological Sulfate Reduction in Deep Subseafloor Sediment of Guaymas Basin

Toshiki Nagakura1, Florian Schubert1, Dirk Wagner1,2, Jens Kallmeyer1* and IODP Exp. 385 Shipboard Scientific Party
  • 1GFZ German Research Centre for Geosciences, Section 3.7 Geomicrobiology, Potsdam, Germany
  • 2Institute of Geosciences, University of Potsdam, Potsdam, Germany

Sulfate reduction is the quantitatively most important process to degrade organic matter in anoxic marine sediment and has been studied intensively in a variety of settings. Guaymas Basin, a young marginal ocean basin, offers the unique opportunity to study sulfate reduction in an environment characterized by organic-rich sediment, high sedimentation rates, and high geothermal gradients (100–958°C km−1). We measured sulfate reduction rates (SRR) in samples taken during the International Ocean Discovery Program (IODP) Expedition 385 using incubation experiments with radiolabeled 35SO42− carried out at in situ pressure and temperature. The highest SRR (387 nmol cm−3 d−1) was recorded in near-surface sediments from Site U1548C, which had the steepest geothermal gradient (958°C km−1). At this site, SRR were generally over an order of magnitude higher than at similar depths at other sites (e.g., 387–157 nmol cm−3 d−1 at 1.9 mbsf from Site U1548C vs. 46–1.0 nmol cm−3 d−1 at 2.1 mbsf from Site U1552B). Site U1546D is characterized by a sill intrusion, but it had already reached thermal equilibrium and SRR were in the same range as nearby Site U1545C, which is minimally affected by sills. The wide temperature range observed at each drill site suggests major shifts in microbial community composition with very different temperature optima but awaits confirmation by molecular biological analyses. At the transition between the mesophilic and thermophilic range around 40°C–60°C, sulfate-reducing activity appears to be decreased, particularly in more oligotrophic settings, but shows a slight recovery at higher temperatures.


As early as the late 19th century microorganisms were anecdotally reported from surficial deep-sea sediment (Fischer, 1894). In the following decades, several studies mentioned the existence of bacteria in marine sediment (e.g., Rittenberg, 1940; ZoBell, 1952). In their seminal study, Morita and ZoBell (1955) showed the existence of viable microorganisms in abyssal clays from the central Pacific down to several meters depth below the seafloor, but evidence for widespread microbial colonization of deep subseafloor sediment down to hundreds of meters was only presented several decades later (Parkes et al., 1994). While Whelan et al. (1985) showed clear indications of metabolic activity at greater depths based on radiotracer measurements, the presence of an abundant and metabolically active microbial community was only proven at the beginning of the 21st century (Schippers et al., 2005).

In subseafloor sediment, the decrease of microbial abundance with depth is mostly the result of decreasing nutrient availability, whereas increasing temperature and pressure only have a minor effect (Jørgensen, 1982; Middelburg, 1989; Møller et al., 2018; Heuer et al., 2020). However, upon deeper burial, the sediment eventually enters the zone of catagenesis. For sediment from Nankai Trough with mostly terrestrially derived organic matter Horsfield et al. (2006) showed that at temperatures above 60°C, the recalcitrant organic matter such as kerogen is thermally cracked, leading to the production of short-chain organic molecules, which can be utilized in situ by microorganisms.

Sulfate-reducing microorganisms (SRM) play a vital role in biogeochemical cycling of sulfur and carbon and therefore are key players in the regulation of global climate (Pester et al., 2012). Sulfate is reduced to hydrogen sulfide which, particularly in marine sediment, further reacts with other ions and organic matter and forms a variety of reduced organic and inorganic sulfur species. The sum of reduced inorganic sulfur species (ΣH2S + FeS + FeS2 + S0) is also called Total Reduced Inorganic Sulfur (TRIS; Howarth, 1979; Howarth and Teal, 1979; Howarth and Giblin, 1983).

Sulfate concentrations are high near the sediment–water interface due to downward diffusion of sulfate from the overlying water column. With increasing depth sulfate concentration decreases as the rate of sulfate consumption exceeds the downward flux. There are two pathways of microbial sulfate reduction:

1. Organoclastic sulfate reduction: 2CH2O + SO42− = 2HCO3 + H2S

2. Methanotrophic sulfate reduction: CH4 + SO42− = HCO3 + HS + H2O

Sulfate-reducing microorganisms can metabolize various carbon substrates, such as fatty acids (Widdel, 1980; Widdel and Pfennig, 1981), aromatic compounds (Widdel, 1980), sugars (Sass et al., 2002), amino acids (Baena et al., 1998), and, in a consortium with archaea, methane (Boetius et al., 2000). The selection of a specific metabolic pathway is based on the availability of substrates. In near-surface sediments, volatile fatty acids (VFAs) are produced by fermentation of macromolecular organic matter. Due to preferential degradation of easily degradable organic matter, the reactivity of the remaining bulk organic matter decreases with increasing burial depth (Middelburg, 1989), leading to lower production rates of VFAs and hence lower sulfate reduction rates (SRR; Hoehler and Jørgensen, 2013).

Methanogenesis is the final step in the degradation of organic matter, once all other electron acceptors with a higher energy yield have been depleted (Froelich et al., 1979). The upward diffusing methane eventually reaches depths where sulfate is still available, the so-called sulfate–methane transition zone (SMTZ) in which sulfate and methane coexist. In the SMTZ, methanotrophic sulfate reduction (i.e., anaerobic oxidation of methane, AOM) takes place. Although the concentration of sulfate is extremely low below the SMTZ, sulfate still exists due to the downwards diffusion of sulfide and re-oxidation to sulfate by reactive iron species. Thus, biological sulfate reduction can occur slowly below the SMTZ (Holmkvist et al., 2011).

With recent improvements in drilling techniques, exploration of the subseafloor biosphere ventured into great depths with correspondingly decreased microbial abundance and metabolic activity (Hoehler and Jørgensen, 2013; Ciobanu et al., 2014; Heuer et al., 2020). The low turnover rates encountered in the deep subsurface require highly sensitive quantification techniques. Since the first measurement of SRR with 35S-radiotracer by Sorokin (1962), the method was improved several times to make it more user friendly, accurate, and sensitive (Howarth and Giblin, 1983; Canfield et al., 1986; Fossing and Jørgensen, 1989; Hsieh and Yang, 1989; Kallmeyer et al., 2004; Røy et al., 2014).

Microbial sulfate reduction occurs over almost the entire known temperature range of life, including the hyperthermophilic range > 80°C (Weber and Jørgensen, 2002). Even at temperatures exceeding 100°C sulfate reduction has been detected (Jørgensen et al., 1992; Elsgaard et al., 1994). High SRR were recorded near hydrothermal vents where a high flux of readily bioavailable low molecular weight carbon compounds fuel high per-cell activity of the SRM, which is necessary to maintain cellular integrity under extreme temperature conditions (Weber and Jørgensen, 2002).

Guaymas Basin, located in the Gulf of California, Mexico, is a young marginal ocean basin of approximately 1,100 km long and 200 km wide that connects to the eastern Pacific Ocean (Figure 1). The high sedimentation rates of >1 mm year−1 result in the mainly biociliceous fine-grained sediment containing abundant organic matter of both marine and terrestrial origin (van Andel, 1964; Curray et al., 1979; Teske et al., 2020). Since thick sediments are covering the active seafloor spreading there are hydrothermal vents on the seafloor and frequent basaltic sill intrusions into the sediment. Geothermal gradients in the subsurface of Guaymas Basin are reaching up to 1,000°C km−1 (Teske et al., 2020). Due to this peculiar geological setting, the bioavailability of organic substrates is expected to not follow the expected decrease as in non-hydrothermal sediments. One of the main objectives of the International Ocean Discovery Program (IODP) Expedition 385 (Guaymas Basin Tectonics and Biosphere) was the investigation of microbial communities and activity in the deep subseafloor biosphere of Guaymas Basin. Detailed drill site descriptions are given by Teske et al. (2020, 2021) (Table 1). Sites U1545C and U1546D have a similar stratigraphy since the distance between these two sites is only about 1.1 km. However, while the sediment at Site U1545C reveals an undisturbed sedimentary profile, the sediment in Site U1546D was intruded by a sill around 350–430 m below seafloor (mbsf), thus these two sites offer a chance to study the impact of sill intrusion on sedimentary biogeochemical cycling.


Figure 1. Sampling sites in Guaymas Basin. Image adapted from Teske et al. (2020). Colored boxed indicate sampling sites where SRR could be measured. The color scheme is used for data plotted in Figures 24. The red line in the insert map is the boundary between the North American and Pacific tectonic plates. The red star in the map indicates the sampling site of Elsgaard et al. (1994).


Table 1. Summary of drill sites of International Ocean Discovery Program (IODP) Exp. 385 (Teske et al., 2020, 2021) from which samples were used for this study.

Sites U1547B and U1548C are located inside and outside of a ringvent (circular hydrothermal mound), respectively. Around these sampling sites, sills intruded into the sediment at relatively shallow depths; ca. 150 mbsf at Site U1547B and ca. 65 mbsf at Site U1548C. This hydrothermally active area was chosen to study the effects of extremely steep geothermal temperature gradients (958°C km−1 at Site U1548C) on biological processes.

Site U1551B is the only site from the southeast region of Guaymas Basin. Sediment at this site is of predominantly terrestrial region. Site U1552B is located close to cold methane seeps and gas hydrates were recovered.

Although SRR were measured previously in Guaymas Basin, the studies focused only on the top 40 cm sediment (Jørgensen et al., 1992; Elsgaard et al., 1994; Weber and Jørgensen, 2002), thus the rates and distribution of microbial sulfate reduction in the deep subseafloor and thermal effect on microbial sulfate reduction are still unclear. We investigated microbial sulfate reduction down to 326 mbsf in subsurface sediment of Guaymas Basin, using 35S radiotracer incubations in the laboratory at approximate in situ temperature and pressure.

Materials and Methods


Core samples were collected from eight drill sites during IODP Exp. 385 (Guaymas Basin Tectonics and Biosphere) from 16 September 2019 to 16 November 2019 (Teske et al., 2020). Figure 1 provides an overview of the sampling area of Exp. 385; detailed information about the sampling sites is given in Table 1. An advanced piston corer (APC)1 can recover soft sediments without disturbing and the half-length APC (HLAPC)2 is employed for firm sediments that are not suitable to use APC. Both coring systems are dedicated to recovering high-quality samples with minimal contamination from drilling fluid, which is a prerequisite for any geomicrobiological or biogeochemical analyses (Kallmeyer, 2017; IODP Tech. Note). Concentrations of pore water methane and sulfate as well as TOC were carried out on board according to established IODP protocols.3 Data were taken from the IODP database.4

Subsampling, Storage, and Sample Processing

Immediately after retrieval of the core, whole round core (WRC) segments were cut off and capped. The WRC was then brought into the ship’s lab, put into gas-tight aluminum foil bags flushed with N2 gas, and stored at ca. 4°C shipboard, in transit, and until use in the home lab. Unfortunately, due to a technical malfunction on board the drill ship, some samples were stored in an oxic atmosphere for several weeks. Samples from Site U1547B were compromised by the extended exposure to oxygen and no reliable SRR measurements could be conducted. Samples from sites U1549B and U1550B also suffered from the exposure to oxygen albeit for much shorter duration. SRR measurement of samples from sites U1549B and U1550B was partially successful but the quality of the data remained inconclusive. The SRR data for these sites, therefore, were also discarded. For this study, we used only SRR measurements from uncompromised samples from sites U1545C, U1546D, U1548C, U1551B, and U1552B.

Preparation of Media

The seawater media for the SRR measurement were prepared as follows, based on Morono et al. (2017): 0.2 g KH2PO4, 0.25 g NH4Cl, 25 g NaCl, 0.5 g MgCl2 × 6H2O, 0.5 g KCl, and 0.15 g CaCl2 × 2H2O, were mixed with 1 L of ultrapure water (UPW). About 3 ml of 0.1% resazurin was added to the media and autoclaved. About 5 ml of Na2S solution (0.12 g Na2S in 10 ml UPW) and 5 ml of NaHCO3 solution (0.84 g NaHCO3 in 10 ml UPW) were added to the media after autoclaving. The media were bubbled with N2/CO2 gas for at least 2 h. After cooling, it was stored in pre-combusted crimp bottles with N2 gas until use within a few days. For all samples from sites U1545C and U1546D, 0.71 g Na2SO4 was also added to set the sulfate concentration to 5 mM. For samples from sites U1548C, U1551B, and U1552B, we approximated the in situ porewater sulfate concentration by adding a separately prepared sterile 1 M Na2SO4 stock solution to those samples.

Control Samples

Killed controls (KC) and media controls (MC) were also prepared and incubated, alongside with the regular samples. For KC, 20% of zinc acetate was added to the sample instead of medium to stop all microbial activity. MC consisted of only the sterile medium and no sediment.

Incubation of Samples

All experiments were carried out at the GFZ German Research Centre for Geosciences, Potsdam, Germany. Inside an anaerobic glove box, 10 g of sample were weighed and put into pre-combusted glass vials. Medium was added and the vial was closed with a black butyl rubber stopper and crimped. To allow for more flexibility of the stopper and improved pressure transmission and hence avoiding breakage of the glass vial upon pressurization or depressurization, we cut off the bottom ca. 5 mm of the stopper. Particularly, at low temperatures, we found that the flexibility of the stoppers was severely reduced, leading to broken vials. We therefore stuck a 3 ml syringe with a cut-off plunger, containing 0.5 ml of medium into each vial (Nauhaus et al., 2002). The syringe can accommodate volume changes irrespective of incubation temperature. The samples were pre-incubated at 4°C overnight at ambient pressure. Then, 5 MBq of 35SO42− were injected into each sample, KC, and MC. Afterward, all vials were put into high-pressure cylinders, which were then placed in a high-pressure thermal gradient block (HPTGB) similar to the design of Kallmeyer et al. (2003). The HPTGB system consists of a thermally insulated aluminum block of 150 cm × 20 cm × 20 cm with three rows of 15 slots each, each slot is holding a stainless-steel high-pressure vessel. Temperature can be adjusted at the two ends of the block, allowing for a thermal gradient of ∆Tmax 107°C, and minimum and maximum temperatures of −5 and 155°C, respectively. Pressure is created by high-pressure liquid chromatography pumps (Sykam, Fürstenfeldbruck, Germany), running at a constant flow rate against a back-pressure regulator (Swagelok, Germany) to prevent pressure fluctuations during thermal equilibration of the samples. The cylinders were pressurized to an approximate in situ pressure of 25 MPa and incubation ran for 10 days. Figure 2 shows the incubation temperature of each sample, together with the downhole temperature gradient. All samples were incubated within ±2°C of their respective in situ temperature. Incubation was terminated by depressurization of the high-pressure cylinder, followed by removal of the crimp vial from the pressure cylinder, opening of the vial, and quantitative transfer of its contents into a 50 ml centrifuge tube preloaded with 5 ml of 20% zinc acetate solution to terminate microbial activity. Remaining sediment pieces were flushed out with 10 ml of 20% zinc acetate solution to transfer all of the incubated sediment into the centrifuge tube. All samples were stored at −20°C until analysis.


Figure 2. Temperature gradients of the different sampling sites of IODP Exp. 385. (A) Downhole temperature gradients of sites U1545 (blue line) and U1546 (red line) measured in situ. Blue circles and red triangles show sampling depth and incubation temperature of each sample from sites U1545C and U1546D, respectively. (B) Downhole temperature gradients of sites U1548 (green line), U1551 (brown line), and U1552 (purple line) measured in situ. Green circles, brown triangles, and purple squares show sampling depth and incubation temperature of each sample from sites U1548C, U1551B, and U1552B, respectively. The black lines in both figures show the average global geothermal gradient of 25°C km−1. Note the different depth scales on the two graphs.

Distillation of the Samples

We used a slightly modified version of the cold chromium distillation of Kallmeyer et al. (2004) to liberate the reduced sulfur species from the sediment. After thawing the samples, they were centrifuged for 10 min at 2,500 × g. For quantification of total radioactivity (aTOT), we mixed 50 μl of the supernatant with 4 ml of scintillation cocktail (Rotiszint® eco plus LSC-Universalcocktail, Carl Roth, Karlsruhe, Germany). The rest of the supernatant was carefully decanted off. The sediment pellet was then quantitatively transferred to the distillation flask and mixed with 15 ml N, N-dimethylformamide (DMF), technical grade. To ensure complete mixing of the sediment with the chemicals, a magnetic stir bar was added to the reaction flask. The flask was connected to a constant stream of nitrogen gas (approximately 5–10 bubbles per second) in order to maintain strictly anaerobic conditions during the distillation. After 10 min of bubbling, the DMF-sediment suspension with N2 gas, 8 ml of 6 M hydrochloric acid (HCl), and 15 ml of 1 M chromium (II) chloride solution were added to the flask via a reagent port. The chemicals will convert all reduced sulfur species (TRIS) to H2S, which is driven out of solution by the stream of nitrogen gas. The produced gas is then led from the flask through a Poly-Ether-Ether-Ketone (PEEK) tube to the citrate trap filled with 7 ml of a buffered citric acid solution (19.3 g citric acid, 4 g NaOH in 1 l H2O, and pH 4) to trap any aerosols potentially containing unreacted 35SO42− radiotracer but let all H2S pass. Finally, the gas is led to a trap containing 7 ml of 5% (w/v) zinc acetate. To prevent overflowing of the zinc acetate trap, a few drops of silicon-based antifoam are added. After 2 h of distillation, the contents of the zinc acetate trap, containing the produced H235S are quantitatively transferred into a 20 ml plastic scintillation vial and mixed with 8 ml scintillation cocktail for quantification of radioactivity by scintillation counting. Each round of distillations also included one distillation blank (DB) containing just a few drops of non-radioactive zinc sulfide carrier and the distillation chemicals mentioned above. The DB was used to detect potential carry-over between distillation runs and therefore tracks the cleanliness of the distillation equipment. Counter blanks (CB) containing just 5% zinc acetate and scintillation cocktail in the same ratios as the samples, are added to each run of the scintillation counter. Counter blanks are required to quantify the background activity, i.e., all signals not associated with radioactivity. We use a HIDEX 600 SL Liquid Scintillation Counter (HIDEX Oy, Finland) with Guard Scintillator. Before the vials are put into the counter, they are vortexed, and the surface of the vial is wiped with 70% ethanol in order to remove any potential contamination on the vial’s surface. Since the samples recovered during the expedition were incubated as slurries with additional medium, the total incubation conditions deviate considerably from in situ conditions. The measured rates should therefore be considered “potential” SRR (pSRR).

Calculation of Sulfate Reduction Rates and Minimum Quantification Limit and Minimum Detection Limit of SRR

The formula of Jørgensen (1978) for calculation of SRR based on radioisotope incubations was designed for whole core incubations, not slurries with added medium. We therefore use a revised version:

SRR = ( [ SO 4 2 ] PW × P SED × V SED + [ SO 4 2 ] MEDIA × V MEDIA ) / V SED × a TRIS / a TOT × 1 / t × 1.06 × 1 , 000 , 000

where SRR is calculated in pmol cm−3 d−1, [SO42−]PW is the sulfate concentration (μmol cm−3) of the sediment porewater, PSED is the porosity of the sediment, VSED is the volume of the sediment (cm3), [SO42−]MEDIA is the sulfate concentration (μmol cm−3) of the media, VMEDIA is the volume of the media (cm3), aTRIS is the radioactivity found in the TRIS fraction, aTOT is total radioactivity used, t is incubation time (d), 1.06 is the correction factor for the expected isotopic fractionation (Jørgensen, 1978), and 1,000,000 is the factor to convert to pmol (Kallmeyer et al., 2004).

Any analytical method, in our case liquid scintillation counting (LSC), has an inherent background and uncertainty. The background (or blank) is a signal to which several factors contribute, but all of them are neither associated with radioactive decay nor with biological turnover of tracer. Ultra-low turnover rates require work at the absolute limit of detection, which in turn requires a strict separation of the background signal and “real” turnover. For assessment of turnover, we use the definitions of minimum quantification limit (MQL) and minimum detection limit (MDL) of Kaiser (1970):

MDL = mean value of blanks

MQL = MDL + k × σb

Where k is the coverage factor associated with the level of confidence, b is the blank and σb is the SD of the background. Both mean value and SD were calculated for all control samples (KC and MC) and blanks (DB and CB), which were processed and measured together with the samples. A coverage factor of k = 3 is chosen to represent a level of confidence of 95% as recommended by Kaiser (1970) and Currie (1968) for one-tailed probabilities, i.e., false positives will only occur above MDL and not below.

The only parameter where the MQL and MDL become relevant is aTRIS, due to the extremely low microbial activity in our samples. As we were using 5 MBq per sample, aTOT is always well above the detection limit. Values of aTOT < MDL are discarded, for values MDL < aTOT < MQL and aTOT > MQL, we calculate a SRR. SRR calculated from values aTOT > MQL represent actual turnover measurements and exclude false positives with a level of confidence of 95%, whereas SRR calculated from values MDL < aTOT < MQL are rates that could be detected but cannot be distinguished from the inherent background of LSC with a sufficient level of confidence. Those rates are plotted as well, but with different symbols. The calculated SRR depends on sulfate concentration and the aTRIS/aTOT ratio, therefore the MQL is different for each sample.


Sulfate Reduction Rates at Sites U1545C and U1546D

The SRR for sites U1545C and U1546D are shown in Figures 3AD. For sites U1545C and U1546D, the original objective in terms of microbiology was to elucidate the impact of sill intrusion on microbial activity at sites with similar sediment composition, TOC content (scattering between 1 and 2.5%) and stratigraphy but different sill intrusion histories. During the expedition downhole, temperature measurements indicated that the sill located at Site U1546D had reached thermal equilibrium with the surrounding sediment (Teske et al., 2021), so there is no local heating effect at present. Both sites have relatively high SRR near the seafloor, with maxima of 5.1 and 48.5 nmol cm−3 d−1 and with minima above MQL of 0.2 and 0.4 pmol cm−3 d−1 for sites U1545C and U1546D, respectively (Figures 3A,B). Sulfate-reducing activity was detectable down to about 300 mbsf at both sites. From the sediment surface down to about 100 mbsf, SRR at Site U1546D are higher than at Site U1545C. From ca. 10 mbsf, SRR drop by several orders of magnitude with depth at Site U1545C, while at Site U1546D SRR decrease more gradually. Below 10 mbsf at Site U1545C and 100 mbsf at Site U1546D, we could detect SRR around 300 fmol cm−3 d−1 and many samples fell below our minimum detection limit. The depths at which SRR fall to near background rates coincide with the respective depths of the SMTZ, which are located around 40 mbsf at Site U1545C and around 110 mbsf at Site U1546D (Figures 3E,F). SRM show metabolic activity over a temperature range from 4 to 74°C (Figures 3C,D), thus the SRM inhabiting the subsurface of Guaymas Basin range from psychrophiles to thermophiles. Interestingly, at both sites, there is a depth interval in which all SRR measurements fell below MQL. At Site U1545C, the SRR < MQL interval reaches from 158.1 mbsf (38°C) to 241.6 mbsf (59°C), whereas at Site U1546D the interval is between 190.7 mbsf (47°C) and 228.4 mbsf (53°C). Above 60°C, in the thermophilic range, SRR start to increase again at both sites (Figures 3C,D).


Figure 3. (A,B) Sulfate reduction rates (SRR) for sites U1545C (blue circles) and U1546D (red triangles) plotted against sampled depth. Closed symbols indicate measurements SRR > MQL and open symbols MDL < SRR < MQL. See the definitions of MQL and MDL in the “Materials and Methods” section. (C,D) SRR for same sites plotted against incubation temperature. (E,F) Concentrations of sulfate and methane. The data were obtained from the Laboratory Information Management System (LIMS) report. Gray bar indicates Sulfate–Methane Transition Zone (SMTZ).

Sulfate Reduction Rates at Sites U1548C, U1551B, and U1552B

The highest SRR value at sites U1548C, U1551B, and U1552B, 387 nmol cm−3 d−1, was measured in a sample from 1.9 mbsf at Site U1548C (Figure 4A), which exhibits the highest geothermal gradient (958°C km−1) among the eight expedition sites. The deepest sample (59.8 mbsf) at this site was located 10 m above a sill and revealed SRR of 4.8–68 pmol cm−3 d−1 at 61°C (Figures 4A,D). All SRR measurements from Site U1548C were above the MQL.


Figure 4. (A–C) SRR for sites U1548C (green circles), U1551B (brown triangles), and U1552B (purple squares) plotted against sampled depth. (D–F) SRR for same sites plotted against incubation temperature. (G–I) Concentrations of sulfate and methane. The data were obtained from the Laboratory Information Management System (LIMS) report. Gray bar indicates Sulfate–Methane Transition Zone (SMTZ). Note the different scales on the graphs.

For sites U1551B and U1552B, SRR in near-surface samples are one to two orders of magnitude lower than that at Site U1548C, revealing maximum values of 34.2 and 46.1 nmol cm−3 d−1, respectively (Figures 4B,C). The temperature ranges of samples retrieved from these two sites are between 3.9 and 7.4°C at Site U1551B and between 4.8 and 16.2°C at Site U1552B but SRR above the MQL could only be detected in samples with temperatures of up to 6.6°C (0.2 pmol cm−3 d−1) and 9.2°C (0.1 pmol cm−3 d−1; Figures 4E,F).

Owing to technical problems with our scintillation counter, we were not able to use the blank measurements (KC, MC, DB, and CB) from the U1548C samples. In order to calculate the MQL, which is crucially important to assess the SRR data, we used blank measurements (KC, MC, DB, and CB) from the Site U1547B samples.

A list of all SRR measurements is provided in the Supplementary Table S1.


Sulfate-Reducing Activity in Deep Subsurface Sediment of Guaymas Basin

We quantified SRR in subsurface sediments from several sites at Guaymas Basin, covering a wide range of geothermal gradients and depositional settings. One aspect of the IODP Exp. 385 was investigating the microbial community in this unique subseafloor environment. Ocean Drilling Program (ODP) Leg 201 was the first ocean drilling project dedicated to the study of subseafloor life. Several sites in the eastern Pacific Ocean and Peru margin were drilled to gain knowledge about the environmental conditions in deep marine subsurface sediments (D'Hondt et al., 2004; Jørgensen et al., 2006). Compared to ODP Leg 201 Site 1226 in the tropical Pacific Ocean (Parkes et al., 2005), SRR are generally higher in Guaymas Basin, particularly, near the seafloor. At depths of tens and hundreds meters below seafloor, SRR are in about the same range (Figure 5). Various reasons contribute to higher turnover rates in Guaymas Basin: firstly, Guaymas Basin sediment is characterized by a generally higher content of organic matter than sediments from open ocean sites (near seafloor samples at sites U1545C and U1546D have >3.5 wt% TOC, whereas at Site 1226 TOC concentrations are <1%). Secondly, the steep geothermal gradients lead to increased availability of organic substrates generated through thermal cracking of otherwise unavailable macromolecular organic matter (Horsfield et al., 2006) at comparatively shallow depths. A third potential factor appears to be local heating around sills to further elevate microbial activity, at least temporarily.


Figure 5. Comparison of SRR in subsurface sediments from the tropical eastern Pacific Ocean (ODP Leg 201, Site 1,226) and Site U1546D.

Compared to the data of Elsgaard et al. (1994), who quantified SRR in the upper 40 cm of hydrothermal sediment from the southern trough of Guaymas Basin (Figure 1), near-seafloor samples from our study revealed similar or higher SRR. The higher SRR could be a result of incubation of our samples at approximate in situ pressure (25 MPa), whereas Elsgaard et al. (1994) carried out all experiments at atmospheric pressure. Using slurries of surface sediment from Guaymas Basin, Kallmeyer et al. (2003) showed that SRR increased by almost an order of magnitude when the incubation was carried out at in situ pressure (ca. 25 MPa) instead of atmospheric pressure. Interestingly, when applying even higher pressure (45 MPa) SRR increased even further, but the increase in SRR when raising the pressure from 25 to 45 MPa was not as pronounced as for the pressure increase from 0.1 to 25 MPa.

Sulfate concentration in the media used for all samples from sites U1545C and U1546D was set to 5 mM, which is lower than in situ porewater sulfate concentrations of near-surface samples and higher for the deep samples. Although the sulfate concentration of the deep samples was increased, SRR of most of the deep samples were below MQL, which we interpret as either electron donor (organic substrate) limitation or a generally very small or metabolically slow SRM community that could not adapt to elevated sulfate levels within the 10 days incubation time.

Abiological sulfate reduction, also termed thermochemical sulfate reduction (TSR), is assumed to occur only at temperatures well over 100°C (Jørgensen et al., 1992; Machel, 2001) and turnover rates are much slower than biological sulfate reduction, we thus assume that SRR measured in our study are exclusively caused by microbial activity.

Effect of Sill Intrusion on the Microbial Sulfate-Reducing Activity

Although a thick sill was predicted from seismic data and observed at Site U1546D, the expected higher geothermal gradient was not observed, with current geothermal gradients at sites U1545C and U1546D being almost identical. This indicates that the sill at Site U1546D has reached thermal equilibrium with its surrounding sediment. The decrease of SRR with depth was steeper at Site U1545C than at Site U1546D and follows the respective decrease in sulfate concentration and thus, the position of the SMTZ, which is much shallower at Site U1545C than at Site U1546D (Figures 3E,F). It appears that presently sulfate availability exerts a much stronger control on SRR than past heating of the sediment. Another possible explanation for the deeper SMTZ at Site U1546D would be that due to past heating of the sediment, the remaining organic matter is more recalcitrant than at site U1545C, and therefore SRM are less active so sulfate can penetrate deeper into the sediment. Detailed organic geochemical analyses of the release potential for short-chain organic compounds (Glombitza et al., 2009) could provide insight into this matter.

Heating apparently has a positive effect on microbial activity. At Site U1548C, which has an extremely steep geothermal gradient of 958°C km−1 SRR are much higher than at all other sites. We acknowledge that sulfate concentrations during incubations of samples from Site U1545C and Site U1546D were all set to 5 mM and therefore deviate more strongly from porewater concentrations than for samples from other sites, where we set the sulfate concentration individually to approximate in situ values (Figures 4GI). Still, these deviations cannot explain differences in rates over several orders of magnitude between the sites, while still maintaining SRR vs. depth profiles that appear to be closely controlled by porewater sulfate concentration, even when incubation conditions differ considerably from in situ conditions.

Site U1548C suggests that heating does have a positive effect on microbial activity. However, the comparison between sites U1545C and U1546D shows that heating caused by sill intrusion at Site U1546D is only temporary. For a more detailed understanding of the influence of sill intrusion and local heating on subsurface microbiology, it would be necessary to recover a suite of sediment samples affected by the entire emplacement and cooling history of sills, plus their non-intruded counterparts for comparison.

Effect of Temperature on SRR

The drill cores from both sites U1545C and U1546D cover intervals with an in situ temperature between ca. 40 and 60°C in which all SRR measurements are below MQL (Figures 3C,D). This temperature is close to the shift between mesophiles (15°C–45°C) and thermophiles (45°C–80°C). In non-hydrothermal subseafloor sediment samples from Nankai Trough (IODP Exp. 370), Heuer et al. (2020) also observed a decrease in cell density in sediment around 50°C and an increase of endospores, which they interpreted as a shift in community composition. It appears that the decrease in SRR over the mesophilic to thermophilic temperature transition is not restricted to a specific site or hydrothermal/non-hydrothermal environment. Using slurries of surficial Guaymas Basin sediment, Elsgaard et al. (1994) could quantify SRR between ca. 40 and 60°C, but for samples without addition of short-chain fatty acids this temperature interval also represents a local minimum of activity. They also showed that addition of carbon sources not only caused a general increase in SRR, but also a shift of the temperature optimum from almost 70°C to <60°C. In our experiments, we did not add any carbon sources to the incubation and the results (Figures 3C,D) show a similar SRR-temperature profile as the data of Elsgaard et al. (1994) for the non-amended slurries, with a local minimum around 40°C–60°C, followed by an increase and local maximum around 65°C.

At sites U1551B and U1552B sulfate-reducing activity is strictly limited to the psychrophilic temperature range as the respective deepest samples from these sampling sites (7.4 and 16.2°C) reveal SRR that are already below the MQL. At least for Site 1552B, these samples roughly fall into a temperature range that marks the shift between psychrophiles (0°C–20°C) and mesophiles (15°C–45°C). At Site U1551B, the temperature range is especially limited and SRR can only be observed up to 6.6°C. The sediment at this site was more influenced by terrigenous sources than at the other sites drilled in Guaymas Basin during Exp. 385 and the thermal gradient is the lowest among the five sampling sites used in this study (Teske et al., 2020). A more detailed characterization of the organic matter is still lacking, so we can only assume that the sedimentary organic material is already more recalcitrant at the time of deposition, causing a more rapid decrease in substrate availability and hence, microbial activity. Additionally, thermal cracking starts at greater depth due to the comparatively lower geothermal gradient, pushing the potential source of substrates for subsurface life even deeper.

Site U1548C, which has the steepest geothermal gradient of all eight sites drilled during Exp. 385 (958°C km−1) forms a stark contrast, in that all measured SRR are above the MQL. SRM are neither limited by electron acceptors, as sulfate concentrations are high throughout the core, nor by electron donors. There is abundant sedimentary organic matter (4.2 wt% of TOC at 2.5 mbsf) and thermal cracking of kerogen due to the onset of catagenesis (60°C) around 60 mbsf might become quantitatively significant in the SMTZ, leading to a supply of both methane and other short-chain organic compounds. However, the temperature at which catagenesis starts and/or becomes quantitatively important depends on the composition of the sedimentary organic matter. As we do not have such information for the IODP Exp. 385 drill cores, we can only assume that the temperature will be roughly in the same range as in Nankai Trough (Horsfield et al., 2006). The ample supply of electron donors is also reflected in the comparatively high SRR throughout the entire core and the lack of a drop in SRR at the mesophilic-thermophilic transition. Elsgaard et al. (1994) also showed in their slurry experiments that carbon addition not only leads to higher SRR, but also less variation in SRR with temperature.

Given the low cell abundances in parts of the cores recovered by Exp. 385 (Morono et al., 2017, pers. comm.) investigations of microbial community structure in these samples is challenging. Thus, our interpretations of changes sulfate reducer community await confirmation by molecular biological analyses.


We measured SRR in deep subseafloor sediment from several sites in Guaymas Basin which were expected to have high microbial activity and abundance compared to other non-hydrothermal subsurface sediments due to their high content of bioavailable organic matter. Sulfate-reducing activity in Guaymas Basin was detected down to nearly 300 mbsf but at most sites only with low turnover rates of approximately 0.5 pmol cm−3 d−1. By contrast, SRR near the seafloor are much higher, reaching 10 to 100s of nmol cm−3 d−1. The highest SRR of 387 nm cm−3 d−1 was found at Site U1548C, where the sediment is very organic-rich and the geothermal gradient is roughly 1,000°C km−1, supposedly leading to thermal cracking of organic matter already at shallow depth. The wide range of the current temperatures in these drill cores requires microbial communities with different temperature optima, ranging from psychrophiles over mesophiles to thermophiles. There is some indication that heating of the sediment leads to elevated microbial activity, but it appears that this effect is only temporarily and ceases once the temperature has decreased again.

Data Availability Statement

The original contributions presented in the study are included in the article/Supplementary Material; further inquiries can be directed to the corresponding author.

Author Contributions

TN, FS, and JK designed study and analyzed data. FS collected samples. TN carried out the experiments. TN wrote manuscript with input from all coauthors. All authors contributed to the article and approved the submitted version.


TN and FS are funded through DFG grants to JK (grant # 670521 and 651694).

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Publisher’s Note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.


The authors would like to thank the crew of IODP Exp. 385 (Guaymas Basin Tectonics and Biosphere) for providing samples and data. Kathleen M. Marsaglia, Armelle Riboulleau, Florian Neumann, Ji-Hoon Kim, Virginia P. Edgcomb, Lucie C. Pastor, Toshiro Yamanaka, Christophe Y. Galerne, Yuki Morono, Tobias W. Höfig, and Andreas P. Teske provided comments on an earlier version of the manuscript.

Supplementary Material

The Supplementary Material for this article can be found online at:

Supplementary Table S1 | List of all sulfate reduction rate measurements.



Baena, S., Fardeau, M. L., Labat, M., Ollivier, B., Garcia, J. L., and Patel, B. K. C. (1998). Desulfovibrio aminophilus sp. nov., a novel amino acid degrading and sulfate reducing bacterium from an anaerobic dairy wastewater lagoon. Syst. Appl. Microbiol. 21, 498–504. doi: 10.1016/S0723-2020(98)80061-1

PubMed Abstract | CrossRef Full Text | Google Scholar

Boetius, A., Ravenschlag, K., Schubert, C. J., Rickert, D., Widdel, F., Gieseke, A., et al. (2000). A marine microbial consortium apparently mediating anaerobic oxidation of methane. Nature 407, 623–626. doi: 10.1038/35036572

PubMed Abstract | CrossRef Full Text | Google Scholar

Canfield, D. E., Raiswell, R., Westrich, J. T., Reaves, C. M., and Berner, R. A. (1986). The use of chromium reduction in the analysis of reduced inorganic sulfur in sediments and shales. Chem. Geol. 54, 149–155. doi: 10.1016/0009-2541(86)90078-1

CrossRef Full Text | Google Scholar

Ciobanu, M.-C., Burgaud, G., Dufresne, A., Breuker, A., Rédou, V., Ben Maamar, S., et al. (2014). Microorganisms persist at record depths in the subseafloor of the Canterbury Basin. ISME J. 8, 1370–1380. doi: 10.1038/ismej.2013.250

PubMed Abstract | CrossRef Full Text | Google Scholar

Curray, J. R., Moore, D., Aguayo, E., Aubry, M., Einsele, G., Fornari, D., et al. (1979). Leg 64 seeks evidence on development of basins. Geotimes 24, 18–20.

Google Scholar

Currie, L. A. (1968). Limits for qualitative detection and quantitative determination. Application to radiochemistry. Anal. Chem. 40, 586–593. doi: 10.1021/ac60259a007

CrossRef Full Text | Google Scholar

D'Hondt, S., Jørgensen, B. B., Miller, D. J., Batzke, A., Blake, R., Cragg, B. A., et al. (2004). Distributions of microbial activities in deep subseafloor sediments. Science 306, 2216–2221. doi: 10.1126/science.1101155

PubMed Abstract | CrossRef Full Text | Google Scholar

Elsgaard, L., Isaksen, M. F., Jørgensen, B. B., Alayse, A.-M., and Jannasch, H. W. (1994). Microbial sulfate reduction in deep-sea sediments at the Guaymas Basin hydrothermal vent area: influence of temperature and substrates. Geochim. Cosmochim. Acta 58, 3335–3343. doi: 10.1016/0016-7037(94)90089-2

CrossRef Full Text | Google Scholar

Fischer, B. (1894). Die Bakterien des Meeres nach den Untersuchungen der Plankton-Expedition unter gleichzeitiger Berücksichtigung einiger älterer und neuerer Untersuchungen Ergebnisse der Plankton-Expedition, (Kiel and Leipzig: Lipsius and Tischer) 1–83.

Google Scholar

Fossing, H., and Jørgensen, B. B. (1989). Measurement of bacterial sulfate reduction in sediments: evaluation of a single-step chromium reduction method. Biogeochemistry 8, 205–222.

Google Scholar

Froelich, P. N., Klinkhammer, G. P., Bender, M. L., Luedtke, N. A., Heath, G. R., Cullen, D., et al. (1979). Early oxidation of organic matter in pelagic sediments of the eastern equatorial Atlantic: suboxic diagenesis. Geochim. Cosmochim. Acta 43, 1075–1090. doi: 10.1016/0016-7037(79)90095-4

CrossRef Full Text | Google Scholar

Glombitza, C., Mangelsdorf, K., and Horsfield, B. (2009). A novel procedure to detect low molecular weight compounds released by alkaline ester cleavage from low maturity coals to assess its feedstock potential for deep microbial life. Org. Geochem. 40, 175–183. doi: 10.1016/j.orggeochem.2008.11.003

CrossRef Full Text | Google Scholar

Heuer, V. B., Inagaki, F., Morono, Y., Kubo, Y., Spivack, A. J., Viehweger, B., et al. (2020). Temperature limits to deep subseafloor life in the Nankai trough subduction zone. Science 370, 1230–1234. doi: 10.1126/science.abd7934

PubMed Abstract | CrossRef Full Text | Google Scholar

Hoehler, T. M., and Jørgensen, B. B. (2013). Microbial life under extreme energy limitation. Nat. Rev. Microbiol. 11, 83–94. doi: 10.1038/nrmicro2939

PubMed Abstract | CrossRef Full Text | Google Scholar

Holmkvist, L., Ferdelman, T. G., and Jørgensen, B. B. (2011). A cryptic sulfur cycle driven by iron in the methane zone of marine sediment (Aarhus Bay, Denmark). Geochim. Cosmochim. Acta 75, 3581–3599. doi: 10.1016/j.gca.2011.03.033

CrossRef Full Text | Google Scholar

Horsfield, B., Schenk, H. J., Zink, K., Ondrak, R., Dieckmann, V., Kallmeyer, J., et al. (2006). Living microbial ecosystems within the active zone of catagenesis: implications for feeding the deep biosphere. Earth Planet. Sci. Lett. 246, 55–69. doi: 10.1016/j.epsl.2006.03.040

CrossRef Full Text | Google Scholar

Howarth, R. W. (1979). Pyrite: its rapid formation in a salt marsh and its importance in ecosystem metabolism. Science 203, 49–51. doi: 10.1126/science.203.4375.49

PubMed Abstract | CrossRef Full Text | Google Scholar

Howarth, R. W., and Giblin, A. (1983). Sulfate reduction in the salt marshes at Sapelo Island, Georgia1. Limnol. Oceanogr. 28, 70–82. doi: 10.4319/lo.1983.28.1.0070

CrossRef Full Text | Google Scholar

Howarth, R. W., and Teal, J. M. (1979). Sulfate reduction in a New England salt marsh. Limnol. Oceanogr. 24, 999–1013. doi: 10.4319/lo.1979.24.6.0999

CrossRef Full Text | Google Scholar

Hsieh, Y. P., and Yang, C. H. (1989). Diffusion methods for the determination of reduced inorganic sulfur species in sediments. Limnol. Oceanogr. 34, 1126–1130. doi: 10.4319/lo.1989.34.6.1126

CrossRef Full Text | Google Scholar

Jørgensen, B. B. (1978). A comparison of methods for the quantification of bacterial sulfate reduction in coastal marine sediments. Geomicrobiol J. 1, 11–27. doi: 10.1080/01490457809377721

CrossRef Full Text | Google Scholar

Jørgensen, B. B. (1982). Mineralization of organic matter in the sea bed—the role of sulphate reduction. Nature 296, 643–645. doi: 10.1038/296643a0

CrossRef Full Text | Google Scholar

Jørgensen, B. B., d'Hondt, S. L., and Miller, D. J. (2006). “Leg 201 Synthesis: Controls on Microbial Communities in Deeply Buried Sediments.” in Proceedings of the Ocean Drilling Program, Scientific Results, The Program.

Google Scholar

Jørgensen, B. B., Isaksen, M. F., and Jannasch, H. W. (1992). Bacterial sulfate reduction above 100°C in Deep-Sea hydrothermal vent sediments. Science 258, 1756–1757. doi: 10.1126/science.258.5089.1756

PubMed Abstract | CrossRef Full Text | Google Scholar

Kaiser, H. (1970). Report for analytical chemists. II. Quantitation in elemental analysis. Anal. Chem. 42, 26A–59A.

Google Scholar

Kallmeyer, J. (2017). “Chapter three—contamination control for scientific drilling operations,” in Advances in Applied Microbiology. Vol. 98. eds. S. Sariaslani and G. M. Gadd (Cambridge, San Diego, London, Oxford: Academic Press), 61–91.

Google Scholar

Kallmeyer, J., Ferdelman, T. G., Jansen, K.-H., and Jørgensen, B. B. (2003). A high-pressure thermal gradient block for investigating microbial activity in multiple deep-sea samples. J. Microbiol. Methods 55, 165–172. doi: 10.1016/S0167-7012(03)00138-6

PubMed Abstract | CrossRef Full Text | Google Scholar

Kallmeyer, J., Ferdelman, T. G., Weber, A., Fossing, H., and Jørgensen, B. B. (2004). A cold chromium distillation procedure for radiolabeled sulfide applied to sulfate reduction measurements. Limnol. Oceanogr. Methods 2, 171–180. doi: 10.4319/lom.2004.2.171

CrossRef Full Text | Google Scholar

Machel, H. G. (2001). Bacterial and thermochemical sulfate reduction in diagenetic settings—old and new insights. Sediment. Geol. 140, 143–175. doi: 10.1016/S0037-0738(00)00176-7

CrossRef Full Text | Google Scholar

Middelburg, J. J. (1989). A simple rate model for organic matter decomposition in marine sediments. Geochim. Cosmochim. Acta 53, 1577–1581. doi: 10.1016/0016-7037(89)90239-1

CrossRef Full Text | Google Scholar

Møller, M. H., Glombitza, C., Lever, M. A., Deng, L., Morono, Y., Inagaki, F., et al. (2018). D:L-amino acid modeling reveals fast microbial turnover of days to months in the subsurface hydrothermal sediment of Guaymas Basin. Front. Microbiol. 9:967. doi: 10.3389/fmicb.2018.00967

PubMed Abstract | CrossRef Full Text | Google Scholar

Morita, R. Y., and ZoBell, C. E. (1955). Occurrence of bacteria in pelagic sediments collected during the mid-Pacific expedition. Deep-Sea Res. 3, 66–73. doi: 10.1016/0146-6313(55)90036-8

CrossRef Full Text | Google Scholar

Morono, Y., Inagaki, F., Heuer, V., Kubo, Y., Maeda, L., Bowden, S., et al. (2017). “Expedition 370 methods.” in Proceedings of the International Ocean Discovery Program 370.

Google Scholar

Nauhaus, K., Boetius, A., Krüger, M., and Widdel, F. (2002). In vitro demonstration of anaerobic oxidation of methane coupled to sulphate reduction in sediment from a marine gas hydrate area. Environ. Microbiol. 4, 296–305. doi: 10.1046/j.1462-2920.2002.00299.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Parkes, R. J., Cragg, B. A., Bale, S. J., Getlifff, J. M., Goodman, K., Rochelle, P. A., et al. (1994). Deep bacterial biosphere in Pacific Ocean sediments. Nature 371, 410–413. doi: 10.1038/371410a0

CrossRef Full Text | Google Scholar

Parkes, R. J., Webster, G., Cragg, B. A., Weightman, A. J., Newberry, C. J., Ferdelman, T. G., et al. (2005). Deep sub-seafloor prokaryotes stimulated at interfaces over geological time. Nature 436, 390–394. doi: 10.1038/nature03796

PubMed Abstract | CrossRef Full Text | Google Scholar

Pester, M., Knorr, K.-H., Friedrich, M., Wagner, M., and Loy, A. (2012). Sulfate-reducing microorganisms in wetlands—fameless actors in carbon cycling and climate change. Front. Microbiol. 3:72. doi: 10.3389/fmicb.2012.00072

PubMed Abstract | CrossRef Full Text | Google Scholar

Rittenberg, S. C. (1940). Bacteriological analysis of some long cores of marine sediments. J. Mar. Res. 3, 191–201.

Google Scholar

Røy, H., Weber, H. S., Tarpgaard, I. H., Ferdelman, T. G., and Jørgensen, B. B. (2014). Determination of dissimilatory sulfate reduction rates in marine sediment via radioactive 35S tracer. Limnol. Oceanogr. Methods 12, 196–211. doi: 10.4319/lom.2014.12.196

CrossRef Full Text | Google Scholar

Sass, A., Rütters, H., Cypionka, H., and Sass, H. (2002). Desulfobulbus mediterraneus sp. nov., a sulfate-reducing bacterium growing on mono- and disaccharides. Arch. Microbiol. 177, 468–474. doi: 10.1007/s00203-002-0415-5

PubMed Abstract | CrossRef Full Text | Google Scholar

Schippers, A., Neretin, L. N., Kallmeyer, J., Ferdelman, T. G., Cragg, B. A., John Parkes, R., et al. (2005). Prokaryotic cells of the deep sub-seafloor biosphere identified as living bacteria. Nature 433, 861–864. doi: 10.1038/nature03302

PubMed Abstract | CrossRef Full Text | Google Scholar

Sorokin, Y. I. (1962). Experimental investigation of bacterial sulfate reduction in the Black Sea using S 35. Microbiology 31, 329–335.

Google Scholar

Teske, A. P., Lizarralde, D., and Höfig, T. W. (2020). “International Ocean Discovery Program Expedition 385 Preliminary Report.”

Google Scholar

Teske, A., Lizarralde, D., Höfig, T., Aiello, I., Ash, J., Bojanova, D., et al. (2021). “Expedition 385 summary.” in Guaymas Basin Tectonics and Biosphere. Teske, A., Lizarralde, D., Höfig, TW and the Expedition 385.

Google Scholar

Van Andel, T. H. (1964). “Recent Marine Sediments of Gulf of California: PART 2.”

Google Scholar

Weber, A., and Jørgensen, B. B. (2002). Bacterial sulfate reduction in hydrothermal sediments of the Guaymas basin, gulf of California, Mexico. Deep-Sea Res. I Oceanogr. Res. Pap. 49, 827–841. doi: 10.1016/S0967-0637(01)00079-6

CrossRef Full Text | Google Scholar

Whelan, J. K., Oremland, R., Tarafa, M., Smith, R., Howarth, R., and Lee, C. (1985). “Evidence for sulfatereducing and methane producing microorganisms in sediments from sites 618, 619, and 622,” in Initial reports of the deep sea drilling project. eds. A. H. Bouma, J. M. Coleman, and A. W. Meyer (Washington, DC: US Printing Office), 767–775.

Google Scholar

Widdel, F. (1980). “Anaerober Abbau von Fettsäuren und Benzoesäure durch neu isolierte Arten sulfat-reduzierender Bakterien.” PhD Thesis. Germany: Georg-August-Universität Göttingen.

Google Scholar

Widdel, F., and Pfennig, N. (1981). Studies on dissimilatory sulfate-reducing bacteria that decompose fatty acids. Arch. Microbiol. 129, 395–400. doi: 10.1007/BF00406470

PubMed Abstract | CrossRef Full Text | Google Scholar

ZoBell, C. E. (1952). Bacterial life at the bottom of the Philippine trench. Science 115, 507–508. doi: 10.1126/science.115.2993.507

PubMed Abstract | CrossRef Full Text | Google Scholar

Keywords: sulfate reduction, subsurface life, deep biosphere, thermophiles, Guaymas Basin

Citation: Nagakura T, Schubert F, Wagner D, Kallmeyer J (2022) Biological Sulfate Reduction in Deep Subseafloor Sediment of Guaymas Basin. Front. Microbiol. 13:845250. doi: 10.3389/fmicb.2022.845250

Received: 29 December 2021; Accepted: 01 February 2022;
Published: 03 March 2022.

Edited by:

Andreas Teske, University of North Carolina at Chapel Hill, United States

Reviewed by:

Doug LaRowe, University of Southern California, United States
Alexey Kamyshny, Ben-Gurion University of the Negev, Israel

Copyright © 2022 Nagakura, Schubert, Wagner and Kallmeyer. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Jens Kallmeyer,

These authors have contributed equally to this work