Skip to main content
mSystems logoLink to mSystems
. 2023 Aug 14;8(4):e00537-23. doi: 10.1128/msystems.00537-23

Redox gradient shapes the abundance and diversity of mercury-methylating microorganisms along the water column of the Black Sea

Léa Cabrol 1,2,, Eric Capo 3,4,5,, Daan M van Vliet 6,7, F A Bastiaan von Meijenfeldt 8, Stefan Bertilsson 4, Laura Villanueva 8,9, Irene Sánchez-Andrea 6, Erik Björn 10, Andrea G Bravo 3, Lars-Eric Heimburger Boavida 1
Editor: Michael S Rappe11
PMCID: PMC10469668  PMID: 37578240

ABSTRACT

In the global context of seawater deoxygenation triggered by climate change and anthropogenic activities, changes in redox gradients impacting biogeochemical transformations of pollutants, such as mercury, become more likely. Being the largest anoxic basin worldwide, with high concentrations of the potent neurotoxic methylmercury (MeHg), the Black Sea is an ideal natural laboratory to provide new insights about the link between dissolved oxygen concentration and hgcAB gene-carrying (hgc+) microorganisms involved in the formation of MeHg. We combined geochemical and microbial approaches to assess the effect of vertical redox gradients on abundance, diversity, and metabolic potential of hgc+ microorganisms in the Black Sea water column. The abundance of hgcA genes [congruently estimated by quantitative PCR (qPCR) and metagenomics] correlated with MeHg concentration, both maximal in the upper part of the anoxic water. Besides the predominant Desulfobacterales, hgc+ microorganisms belonged to a unique assemblage of diverse—previously underappreciated—anaerobic fermenters from Anaerolineales, Phycisphaerae (characteristic of the anoxic and sulfidic zone), Kiritimatiellales, and Bacteroidales (characteristic of the suboxic zone). The metabolic versatility of Desulfobacterota differed from strict sulfate reduction in the anoxic water to reduction of various electron acceptors in the suboxic water. Linking microbial activity and contaminant concentration in environmental studies is rare due to the complexity of biological pathways. In this study, we disentangle the role of oxygen in shaping the distribution of Hg-methylating microorganisms consistently with MeHg concentration, and we highlight their taxonomic and metabolic niche partitioning across redox gradients, improving the prediction of the response of marine communities to the expansion of oxygen-deficient zones.

IMPORTANCE

Methylmercury (MeHg) is a neurotoxin detected at high concentrations in certain marine ecosystems, posing a threat to human health. MeHg production is mainly mediated by hgcAB gene-carrying (hgc+) microorganisms. Oxygen is one of the main factors controlling Hg methylation; however, its effect on the diversity and ecology of hgc+ microorganisms remains unknown. Under the current context of seawater deoxygenation, mercury cycling is expected to be disturbed. Here, we show the strong effect of oxygen gradients on the distribution of potential Hg methylators. In addition, we show for the first time the significant contribution of a unique assemblage of potential fermenters from Anaerolineales, Phycisphaerae, and Kiritimatiellales to Hg methylation, stratified in different redox niches along the Black Sea gradient. Our results considerably expand the known taxonomic diversity and ecological niches prone to the formation of MeHg and contribute to better apprehend the consequences of oxygen depletion in seawater.

KEYWORDS: mercury methylation, diversity, hgcAB gene, metagenomics, redoxcline, niche partitioning, qPCR, MAGs

INTRODUCTION

Decades of anthropogenic emissions and widespread atmospheric dispersal make mercury (Hg) a contaminant of global concern (1). Hg can be transformed into the neurotoxin methylmercury (MeHg) and detected at high concentrations in certain marine ecosystems, where it bioaccumulates and biomagnifies, ultimately causing severe risks for humans (2). The methylation of HgII to MeHg is mainly mediated by microorganisms and has primarily been described in anoxic environments such as wetlands, sediments, rice paddies, or animal gut (3). Aside from the sine qua non presence and activity of microorganisms producing MeHg, Hg methylation is also controlled by Hg bioavailability, organic matter composition, and oxygen concentrations. Relatively high MeHg concentrations and Hg methylation potential have been reported in oxygen-deficient water columns (4, 5). However, there is still limited knowledge about the microbial key players involved in Hg methylation in marine ecosystems and the environmental conditions constraining their activity (6).

Microbial methylation of Hg has been shown to involve and rely on the enzyme coded by the gene pair hgcA and hgcB (7). Microorganisms that harbor these genes (hgcAB gene-carrying [hgc+] microorganisms), and the methylation capacity they provide, have been identified across diverse microbial lineages and different environments (8 - 10). Most cultivated lineages with experimentally validated Hg methylation capacity have been affiliated to sulfate-reducing, iron-reducing, and/or syntrophic-fermenting bacteria from Desulfobacterota and Firmicutes, as well as to methanogenic Archaea (3, 11, 12). Recent high-throughput sequencing analyses, including the reconstruction of metagenome-assembled genomes (MAGs) from environmental samples, have revealed a broader diversity of putative Hg methylators including previously unknown and largely uncultured hgc+ microorganisms such as Planctomycetota, Verrucomicrobiota, Chloroflexota, and Nitrospirota (13 - 16), some of them being found abundantly in coastal and “dead zone” systems, such as the fully anoxic bottom waters of a stratified fjord (10), a seasonally anoxic fjord (Saanich Inlet) (17), and oxygen-deficient brackish water from the Baltic Sea (18, 19). These studies corroborate that the main methylators differ between ecosystems and along dominant redox gradients.

In the ocean, climate change and human activities lead to current—and further expected—seawater deoxygenation and expansion of oxygen-deficient zones (20). The modification of redox gradients can dramatically affect microbial and biogeochemical cycles, including Hg transformations. Since the Black Sea is the largest and deepest permanently euxinic (anoxic and sulfidic conditions) stratified basin worldwide, with stable redox gradients extending over several tens of meters (21, 22), it is a promising target to study the partitioning of Hg-methylating microorganisms over contrasted redox niches. A stable permanent pycnocline prevents mixing and exchange between the upper oxygenated layers and anoxic deep waters, separated by a suboxic water layer extending from 75 to 120 m (down to 240 m at certain coastal stations) (23). In the Black Sea water column, high concentrations of MeHg concentrations have been reported in the suboxic and anoxic water layers (24, 25). The high horizontal (isopycnal) homogeneity of the Black Sea has been demonstrated, in terms of microbial community composition (26), hydrography (27), and geochemistry, including Hg chemistry (25). However, the microorganisms involved in Hg methylation in the Black Sea water column have not been identified yet, neither the effect of the vertical stratification on their composition. As reported for other euxinic systems (e.g., Baltic Sea, Cariaco Basin, Saanich Inlet), it is plausible that the vertical gradient of oxygen and HS concentrations in the Black Sea shapes the distribution of microbial communities, including those involved in MeHg formation, as well as their associated metabolic and biogeochemical functions (22, 28 - 30).

In this study, we aimed to determine the impact of the vertical redox gradient on the microorganisms potentially responsible for Hg methylation in the water column of the Black Sea. We combined geochemical and molecular data obtained from two sampling campaigns conducted in 2013 that had resulted in the previous characterization of (i) high-resolution Hg and MeHg concentrations throughout full water column transects (25) and (ii) specific (sulfur- and organic matter-linked) microbial metabolisms through genome-centric metagenomics (29 - 31). We used several molecular analyses including 16S rRNA amplicon sequencing, metagenomics, and clade-specific quantitative PCR of the hgcA gene, at different depths, to determine whether the highest concentrations of MeHg observed in the anoxic water layers of the Black Sea were explained by the presence, abundance, and metabolic traits of hgc+ microorganisms. The present study is novel in revealing the oxygen-dependent niche partitioning of diverse microorganisms potentially capable of Hg methylation in the Black Sea, consistently with measured MeHg concentrations.

MATERIALS AND METHODS

Sampling campaigns

Two complementary field cruises were conducted almost simultaneously in June–July 2013 in the Black Sea with the vessel R/V Pelagia to obtain (i) Hg chemistry data, hgcA quantitative PCR (qPCR), and 16S rRNA gene amplicon sequencing data (MEDBlack cruise) and (ii) planktonic metagenomes (Phoxy cruise). Following the definitions in Stewart et al. (32) and the vertical discretization model of Rosati et al. (25), the water column was decomposed into three redox layers: the oxic layer (OL, from 0 to 75 m depth, characterized by O2 concentrations between 30 and 300 µM and undetectable HS concentrations), the suboxic layer (SOL, from 75 to 120 m depth, characterized by dissolved O2 concentrations <20 µM and HS concentrations <5 µM), and the anoxic layer (AOL, below 120 m depth, characterized by undetectable O2 concentrations and HS concentrations between 15 and 400 µM).

The MEDBlack cruise was conducted from 13 to 25 July 2013 and occupied 12 stations along a west-to-east transect. In the present work, we include five stations (1, 2, 5, 6, and 9, according to previous nomenclature [25]; Fig. 1). For microbiology, water samples were collected from three water depths: OL (30–50 m), SOL (90–110 m, except coastal station 6 sampled at 180 m depth), and AOL (140–150 m, except coastal station 6 sampled at 250 m depth) (exact sampling depths are provided in Data Sheet S1A). Samples were filtered with in situ Stand Alone Pump System (Challenger Oceanic, from NOC, Southampton) equipped with two 293 mm diameter filters: a Petex nylon mesh pre-filter (51 µm; 150 µm for station 1) and a polycarbonate filter (1 µm) further stored at −20°C.

Fig 1.

Fig 1

Locations of stations sampled in the Black Sea during the MEDBlack cruise and analyzed in this study (black dots). The star indicates station 2 which was also sampled during the Phoxy cruise for metagenomics analysis. The exact coordinates are provided in Data Sheet S1A.

The Phoxy cruise 64PE371 was conducted on 9 and 10 June 2013 in the western gyre of the Black Sea. Suspended particulate matter was collected from 15 depths across the oxygen gradient in the water column (from 50 to 2,000 m depth) at sampling station 2 (42.89 N, 30.67 E, 2,107 m depth [Fig. 1], at 72 km from the MEDBlack station 2 and visited 35 days earlier) with McLane WTS-LV in situ pumps (McLane Laboratories Inc., Falmouth, MA, USA) on pre-combusted glass fiber filters with 142 mm diameter and 0.7 µm nominal pore size, further stored at −80°C. One sample from the Phoxy cruise belonged to the OL (50 m depth), eight samples to the SOL (70–110 m depth), and six samples to the AOL (130–2000,m depth).

Physicochemical measurements

For the Phoxy cruise, chemical parameters included the dissolved concentrations of O2, HS, NH4+, NO2, and NO3 (Data Sheet S1B). Dissolved O2 concentration was measured by a conductivity-temperature-depth (CTD) probe equipped with a Seabird SBE 43 electrochemical O2 sensor which was calibrated against on-deck Winkler titrations, with a detection limit of 2 µM. Nutrients concentrations were measured on a QuAAtro autoanalyzer with a detection limit of 0.26, 0.031, 0.011, 0.007, and 0.008 µM for HS, NH4+, NO3, NO2, and PO43−, respectively (33). A summary of available and new data for both campaigns is provided in Table 1.

TABLE 1.

Description of samples included in this study and summary of the main measured geochemical parameters, available from Rosati et al. (25) (for MEDBlack samples) and from Sollai et al. (33) (for Phoxy cruise)a

Sample name Cruise campaign Sampling depth (m) Concentrations of dissolved elements Method
O2 (µM) HS (µM) NH4+ (µM) PO43− (µM) tHg (pM) MeHg (pM)
F1-OL MEDBlack 55.5 142.4 <LoD <LoD 0.7 1.4 0.2 MB, qPCR
F1-SOL MEDBlack 85.7 3.4 <LoD 0.1 0.9 1.4 0.1 MB, qPCR
F1-AOL MEDBlack 145.3 <LoD 19.3 13.5 5.0 3.1 0.8 MB, qPCR
F2-OL MEDBlack 24.2 423.0 <LoD 0.2 <LoD 3.3 0.1 MB, qPCR
F2-SOL MEDBlack 99.5 1.8 <LoD 3.9 6.2 1.6 0.2 MB, qPCR
F2-AOL MEDBlack 144.8 <LoD 22.6 15.2 5.0 5.3 0.8 MB, qPCR
F9-OL MEDBlack 45.8 213.1 <LoD 0.1 0.8 2.2 0.1 MB, qPCR
F9-SOL MEDBlack 100.4 1.8 <LoD 2.0 6.6 2.2 0.2 MB, qPCR
F9-AOL MEDBlack 149.6 <LoD 17.7 15.8 4.8 3.6 1.1 MB, qPCR
F5-OL MEDBlack 40.5 373.8 <LoD 0.1 <LoD 2.8 0.1 MB, qPCR
F5-SOL MEDBlack 110.4 1.8 <LoD 3.6 7.0 3.2 0.4 MB, qPCR
F5-AOL MEDBlack 149.4 <LoD 15.3 13.8 4.8 3.3 0.8 MB, qPCR
F6-OL MEDBlack 40.3 377.0 <LoD <LoD <LoD 3.0 0.1 MB, qPCR
F6-SOL MEDBlack 175.0 10.7 <LoD 0.2 3.1 2.9 0.4 MB, qPCR
F6-AOL MEDBlack 250.3 <LoD 36.5 19.2 4.9 3.3 0.8 MB, qPCR
F2-50 Phoxy 50 121.2 <LoD 0.1 0.7 Nd Nd MG
F2-70 Phoxy 70 2.2 <LoD 0.1 1.1 Nd Nd MG
F2-80 Phoxy 80 <LoD <LoD 0.1 1.1 Nd Nd MG
F2-85 Phoxy 85 <LoD <LoD 0.1 0.8 Nd Nd MG
F2-90 Phoxy 90 <LoD <LoD 0.4 2.1 Nd Nd MG
F2-95 Phoxy 95 <LoD <LoD 1.1 4.7 Nd Nd MG
F2-100 Phoxy 100 <LoD <LoD 5.7 7.2 Nd Nd MG
F2-105 Phoxy 105 <LoD 0.9 7.2 7.9 Nd Nd MG
F2-110 Phoxy 110 <LoD 4.6 8.8 6.7 Nd Nd MG
F2-130 Phoxy 130 <LoD 14.7 13.9 5.5 Nd Nd MG
F2-170 Phoxy 170 <LoD 31.6 20.1 4.9 Nd Nd MG
F2-250 Phoxy 250 <LoD 84.7 32.6 5.2 Nd Nd MG
F2-500 Phoxy 500 <LoD 206.3 59.8 6.8 Nd Nd MG
F2-1000 Phoxy 1,000 <LoD 353.8 90.8 7.9 Nd Nd MG
F2-2000 Phoxy 2,000 <LoD 397 100.2 8.4 Nd Nd MG
a

Detailed data sets including additional measured parameters are provided in Data Sheet S1A and B. Nd, non-determined; LoD, limit of detection. The “method” column stands for the molecular methods applied in the current study: MB for metabarcoding, qPCR for quantitative PCR, MG for metagenomics.

For the MEDBlack cruise, available measured physicochemical parameters (Data Sheet S1A) include pressure, temperature, conductivity, fluorescence, salinity, density, and the dissolved concentrations of O2, HS, NH4+, NO2, NO3, PO43−, Si, Fe, DOC, total Hg, and MeHg (sum of mono- and di-MeHg) according to previous protocols (25). Specific analysis of Hg and MeHg is detailed in Supplementaal Information 1.1. The detection limit was 0.025 and 0.001 pM for HgD and MeHgD, respectively. Nutrients, HS, and dissolved O2 concentrations were measured similarly to the Phoxy cruise with the same detection limits. Despite coming from two different cruises, the variability between nutrients, HS, and dissolved O2 concentrations measured in both cruises at similar depths is low (4–14% variability on average).

DNA extractions

From the MEDBlack cruise, DNA was extracted from sections of the 15 filters (i.e., five stations, three depths) with the FastDNA kit and FastPrep homogenizer (MP Biomedicals, Santa Ana, CA, USA) according to the manufacturer instructions. The filter fraction represented 2.5% of the whole filter area, corresponding to approximately 5–13 L of filtered seawater depending on the sampling points (8 L on average). From the Phoxy cruise, DNA was extracted from sections of 15 glass fiber filters (1/8 filter from 50 to 130 m depth and 1/4 from 170 to 2,000 m depth) with the RNA PowerSoil Total Isolation Kit plus the DNA elution accessory (Mo Bio Laboratories, Carlsbad, CA, USA) as previously described (31).

Amplicon sequencing and qPCR estimates of 16S rRNA genes

For the MEDBlack cruise DNA samples, the hypervariable V4-V5 region of the 16S rRNA gene from Bacteria and Archaea was amplified with high-fidelity Phusion Hot Start II DNA polymerase (Thermo Scientific, Waltham, MA, USA) using universal primers 515F and 928R (34) and a two-step PCR protocol (35), as detailed in Supplemental Information 1.2. and Table S1. The correct amplicon size and the absence of non-specific bands were checked by agarose gel electrophoresis. Amplicons were sequenced using a 2 × 250 bp paired-end MiSeq system (Illumina, USA) at the Genotoul platform (Toulouse, France). The raw sequences have been deposited at NCBI GenBank, SRA database, under the BioProject accession number PRJNA895066.

Raw sequences were analyzed on the Galaxy bioinformatics platform through the FROGS pipeline, version 3.2.3, as detailed in the Supplemental Information. Especially, operational taxonomic units (OTUs) were defined by sequence clustering, using the high-resolution SWARM algorithm v3.2.3 (36). After filtering at 0.005% of abundance, OTUs were taxonomically annotated with the SILVA 16S database (version 138.1).

Bacterial and archaeal abundances were quantified in the MEDBlack cruise DNA samples by quantitative PCR with Takyon No Rox SYBR 2X Master Mix (Eurogentec, Seraing, Belgium). Protocol details are provided in Table S1.

Clade-specific hgcA gene qPCR estimates and cloning sequencing of hgcA sequences

In the MEDBlack cruise DNA samples, the hgcA genes of each of the three dominant Hg-methylating clades (Desulfobacterota, Firmicutes, and Archaea) were quantified by qPCR, using clade-specific degenerated qPCR primers (37) and Takyon No Rox SYBR 2X Master Mix (Eurogentec, Seraing, Belgium). The qPCR conditions have been optimized as detailed in the Supplemental Information. All qPCR details and primer sequences are provided in Supplemental Information 1.3. and Table S1.

For Archaea-hgcA, due to the low amplification efficiency and the ambiguity in the melting curves and agarose gel electrophoresis, the correct affiliation of the hgcA amplicons was verified by cloning and sequencing the amplified PCR product, as detailed in Supplemental Information 1.4. Obtained DNA sequences were translated into amino acid sequences and compared with hgcA sequences from the Hg-MATE database (38) and from the 15 metagenomes obtained in the Phoxy cruise (see following section). The sequence analysis (Supplemental Information 1.4 and Fig. S2) showed that hgcA sequences obtained with this primer set clustered with Euryarchaeota and Chloroflexota sequences. Thus, from thereon, hgcA qPCR estimates from Archaea will be referred to hgcA qPCR estimates from Archaea-Chloroflexota.

Metagenomic estimates of hgcA genes

The 15 DNA extracts from the Phoxy cruise were used to prepare TruSeq nano libraries, sequenced with Illumina MiSeq (five samples multiplexed per lane) at Utrecht Sequencing Facility, generating 4.5 × 107 paired-end reads (2 × 250 bp), which were further processed as previously reported (31) and summarized in Supplemental Information 1.5.

hgc homologs were identified and annotated in the amino acid FASTA file (generated from protein-coding genes detected in the metagenomes coassembly), using the HMM profiles of hgcA and hgcB genes derived from the Hg-MATE database v1.01142021 (38) and the function hmmsearch from HMMER 3.2.1 (39). We considered genes with E-values <10−3 as significant hits. To further confirm putative hgcA and hgcB genes (or hgc-like genes) within the HMM search hits, we used the high stringency cutoff defined by Capo et al. (8) by looking for unique conserved motifs from hgcA gene (NVWCA(A/G/S)GK) and performed a manual inspection of the presence of hgcA genes. Coverage values of hgcA genes were calculated as the number of reads mapped to the gene divided by its length (base pairs, bp) and were further normalized by dividing them by the coverage values of the marker gene rpoB. The rpoB genes were detected using the function hmmsearch from HMMER 3.2.1 (39) and HMM profile TIGR02013.hmm for bacterial rpoB genes and applying the trusted cutoff provided in HMM files.

The obtained hgcA homologs, translated in amino acid sequences, were taxonomically affiliated through a phylogenetic analysis, by placing them onto the HgcA reference tree using a pplacer approach (40). The construction of the reference tree was based on the reference package “hgcA” from Hg-MATE database v1, according to the protocol in the README.txt of the Hg-MATE database (38) and in Capo et al. (8), as detailed in Supplemental Information 1.5. As a complement to this community-level analysis, metagenome-assembled genomes generated from the same previously published metagenomes (30, 31) were screened for hgc genes. The hgc genes found in MAGs were taxonomically identified using the MAG phylogeny and taxonomy (Data Sheet S1D).

Data analysis

The qPCR estimates were statistically analyzed by two-way analysis of variance (ANOVA) with the aov function (R software). The selected environmental parameters for correlation analysis were the concentrations of dissolved O2, HS, and MeHg. Spearman correlation plots were obtained using the functions rcorr and corrplot from the R packages Hmisc and corrplot, respectively. Shannon diversity indices were calculated with the estimate_richness function in the vegan R package. Principal coordinates analysis (PCoA) was performed applying the function wcmdscale to Bray-Curtis dissimilarity matrixes built with the function vegdist from the 16S rRNA gene-based OTU abundance table and the hgcA gene abundance (normalized coverage values) in the R package vegan. The discriminant hgcA genes explaining the most the clustering of hgc+ community according to depth zones were identified by linear discriminant analysis (run_lefse function, microbiomeMarker package) with cumulative sum scaling normalization and 100 bootstraps.

RESULTS

Mercury and microbial community stratification along water depth and oxygen gradient

Hg and MeHg profiles revealed a strong depth stratification, homogeneous across the whole basin (Fig. S1). In stations 1, 2, and 5, the MeHg concentration was always maximal at the same depth (130 m) reaching 0.83–1.13 pM, which represents 32%–48% of tHg at this depth. The MeHg concentration then decreased down to 250 m depth and remained relatively stable in deeper waters (0.50–0.65 pM on average below 250 m depth, representing 19%–26% of tHg).

Microbial community structure was homogeneous horizontally across the Black Sea basin, but vertically stratified across water depth and oxygen concentrations. Considering the MEDBlack samples, bacterial abundances based on qPCR of the bacterial 16S rRNA gene did not significantly differ along the west-to-east transect (two-way ANOVA, P = 0.4) but were significantly impacted by sampling depth (two-way ANOVA, P < 0.001) (Fig. 2A; Data Sheet S1A). The highest bacterial abundances (7.8 108 16S copies L−1 on average) were observed in the OL (30–50 m depth), being one order of magnitude higher than in the AOL (140–250 m depth). Archaeal abundances measured by qPCR also varied with depth (P = 0.001), but showed a reverse stratification pattern from bacteria (Fig. 2B) as detailed in Supplemental Information 2.1.

Fig 2.

Fig 2

Stratification of microbial profiles in the Black Sea water column. Data from the five sampling stations have been averaged for oxic (OL, 25–50 m), suboxic (SOL, 85–110 m, except station 6 at 175 m), and anoxic (AOL, 145–250 m) layers. (A) qPCR quantification of bacterial 16S rRNA gene, per filtered volume of seawater. (B) qPCR quantification of archaeal 16S rRNA gene, per filtered volume of seawater. (C) Diversity of total microbial community based on Shannon index, computed from 16S rRNA gene amplicon sequences. (D) Taxonomic composition of microbial communities at the phylum level, representing the 11 most abundant phyla. In panels A to C, the bold line of each boxplot shows the median, while upper and lower limits of the boxes represent the first and third quartiles, respectively. The whiskers are maximum and minimum values and the dots show the outliers. For panel D, for each phylum, the averages and standard deviations calculated per water layer are provided in Data Sheet S1E. The taxonomic composition of the five individual sampling stations across the Black Sea basin is shown in Fig. S3 (at the phylum level) and the detailed OTU composition is provided in Data Sheet S1C.

The taxonomic composition (Fig. S3) and the structure (Fig. 3A) of the prokaryotic community was similar across the west-east transect, as confirmed by the non-significant effect of sampling station on the community structure permutational multivariate analysis of variance (PERMANOVA P > 0.1) and Shannon diversity (ANOVA, P = 0.16). For all stations, OL communities were dominated by Cyanobacteria representing 70% of prokaryotes (Fig. 2D; Fig. S3; Data Sheet S1C and E). SOL and AOL were significantly more diverse (ANOVA, P < 0.001, Fig. 2C), dominated by Planctomycetota (29%–47% of the prokaryotes), Bacteroidota (13%–15%), and Desulfobacterota (7%–9%) (Supplemental Information 2.1).

Fig 3.

Fig 3

Depth stratification of prokaryotic and hgc+ communities in relation with environmental gradients and Hg-related variables. (A and B) PCoA plots based on Bray-Curtis dissimilarity showing the structure of the overall prokaryotic community (A; MEDBlack cruise samples) and of the hgc+ microbial groups (B; Phoxy cruise samples). The dot color denotes the HS concentrations measured in the same samples. The color of the sample name label corresponds to the three water-depth zones: the oxic (OL, gray), suboxic (SOL, light blue), and anoxic (AOL, dark blue) water layers. (C) Correlation plots based on Spearman correlation coefficients between environmental parameters (O2, HS, and MeHg concentrations) and qPCR and metagenomic (MG) estimates of hgcA genes from different microbial groups. Only significant relationships (P < 0.05) are displayed. No MeHg measurements were done during the Phoxy cruise (metagenome samples).

Clade-specific hgcA genes measured by qPCR are more abundant in the anoxic layer

Abundance of hgcA genes was quantified by qPCR for each of the well-known Hg-methylating clades Desulfobacterota, Firmicutes, and Archaea-Chloroflexota (37) (see Supplemental Information 1.4 for the clade definition). Analogous to 16S rRNA gene counts, absolute hgcA counts from Desulfobacterota, Firmicutes, and Archaea-Chloroflexota were similar along the west-to-east transect of the Black Sea (two-way ANOVA, P > 0.90), but strongly stratified over depth (two-way ANOVA, P < 0.0001). Tracking the MeHg concentration profiles (Fig. 4A; Fig. S1), the highest hgcA counts were found in the AOL for all three clades, reaching on average 9.0 ± 3.0 103, 6.1 ± 1.4 106, and 5.6 ± 1.5 106 copies L−1 of seawater for Firmicutes, Desulfobacterota, and Archaea-Chloroflexota, respectively (Fig. 4B; Data Sheet S1A). The hgcA counts were between 12 and 31 times lower in the OL. In the SOL and AOL, hgcA counts from Desulfobacterota and Archaea-Chloroflexota were similar, exceeding that of Firmicutes by one to three orders of magnitude.

Fig 4.

Fig 4

Vertical stratification of MeHg concentrations and hgcA gene abundances in the Black Sea water column. Data from the five sampling stations have been averaged for oxic (OL, 25–50 m), suboxic (SOL, 85–110 m, except station 6 at 175 m), and anoxic (AOL, 145–250 m) layers. (A) Dissolved concentration of MeHg. (B) qPCR quantification of hgcA gene, indicator of Hg methylation ability, for Firmicutes, Desulfobacterota, and Archaea-Chloroflexota, in copies per seawater filtered volume. The bold line of each boxplot shows the median, while upper and lower limits of the boxes represent the first and third quartiles, respectively. The whiskers are maximum and minimum values and the dots show the outliers. The values for the five individual sampling stations are provided in Data Sheet S1A, as well as the relative hgcA counts (normalized by total prokaryotic abundance).

The higher abundance of hgcA genes in the AOL was not only observed for absolute hgcA counts, but also for relative hgcA counts (normalized by summed bacterial and archaeal 16S gene counts, Data Sheet S1A), which contrasts with the pattern observed for total bacteria and indicates a clear enrichment of potential Hg methylators in oxygen-deficient deeper waters. Relative hgcA counts from Desulfobacterota represented 4.8%–9.8% of the prokaryotes in the AOL, 0.5%–2.9% in the SOL, and <0.2% in the OL. hgcA counts from Archaea-Chloroflexota followed a similar depth pattern, representing 4.3%–6.9% of the prokaryotes in the AOL and 0.8%–2% in the SOL, while not detected in the OL. Finally, Firmicutes-hgcA genes accounted for <0.02% of the prokaryotes in all layers. The specificity of the Archaea-Chloroflexota hgcA primers is further evaluated and discussed in the Supplemental Information.

hgc genes in the water column are affiliated to diverse taxa with specific niches

A total of 91 hgcA genes were found in the Black Sea metagenome co-assembly, including 14 genes found next to hgcB genes on the same contig (Data Sheet S1D). Among them, 15 hgcA genes were found in MAGs affiliated to various orders of Desulfobacterota (Desulfobacterales, Desulfobulbales, unclassified), Chloroflexota (Anaerolineales), Bacteroidota (Bacteroidales), Planctomycetota (Phycisphaerales), Verrumicrobiota (Kiritimatiellales), and KSB1 candidate division (unclassified) (Fig. 5A). Among Desulfobacterota, the hgc+ MAGs were identified as uncultured species of UDesulfacyla, UDesufatibia, UDesulfobia, and Desulfobacula. From the alignment to the Hg-MATE database, the remaining 76 unbinned hgcA genes were affiliated predominantly to Desulfobacterota (32), Planctomycetota (14, among which 4 Phycisphaerae), Verrucomicrobiota (9 Kiritimatiellales), Chloroflexota (8 Anaerolineales), and various microbial lineages (Data Sheet S1D).

Fig 5.

Fig 5

A diverse microbial community potentially able to methylate Hg in the Black Sea water column. (A) Unrooted hgcA phylogenetic tree showing the diversity of hgc+ microorganisms from the Black Sea water column compared to the reference sequences from the Hg-MATE database. The 15 binned hgcA genes found in MAGS are denoted in the figure by their ID number in red (see “gene_id” in Data Sheet S1D). The other 77 unbinned hgcA genes are listed in Data Sheet S1D; after examination of their placement on the phylogenetic tree, they were assigned to a taxonomic cluster denoted from “a” to “h” (indicated in the column “Corresponding cluster in hcgA tree” of Data Sheet S1D). For clarity purpose, only the cluster letter is shown on the tree (blue circles at the basis of each group) instead of the 77 sequences. The reference phylogenetic tree was provided by the Hg-MATE database using hgcA sequences from (i) pure culture/environmental microbial isolates (204 sequences), (ii) single-cell genome sequences (29 sequences), and (iii) metagenome-assembled genomes (787 sequences), as detailed in Materials and Methods and Supplemental Information 1.5. (B) Vertical distribution of MG-estimated coverage values of hgcA genes normalized by rpoB coverage values along the water column depth in the Black Sea. The corresponding compartmentation into oxic (OL), suboxic (SOL), and anoxic (AOL) layers is shown on the left axis. Color code corresponds to taxonomic affiliation.

The metagenome-estimated (MG-estimated) abundance and diversity of hgcA genes were both strongly stratified along the Black Sea water column (Fig. 5B; Data Sheet S1B). This was in line with the qPCR results for clade-specific hgcA genes, although samples for metagenomic analysis were collected with a higher vertical resolution (15 depths). hgcA genes were barely detected in the OL and at the top of the SOL (<0.1% of the reads above 70 m depth). The abundance of hgcA genes (i.e., normalized coverage values) gradually increased over depth, reaching the highest value at the SOL-AOL transition (130 m depth, 14.3% of the total hgcA abundance). In deeper water layers, hgcA abundance decreased to 8.4%–9.9% at 1,000–2,000 m depth. MG-derived hgcA genes from Desulfobacterota were predominant in both the SOL (28.3%–58.4% of all hgcA genes) and the AOL (33.0%–53.8%). The second most abundant MG-derived hgcA sequences belonged to Anaerolineales and Phycisphaerae and predominated in the AOL (representing, respectively, 15.1 ± 6.8% and 6.4 ± 3.1% of all hgcA in this layer), while hgcA genes from Kiritimatiellales and Bacteroidales predominated in the SOL (12.9 ± 10.1% and 5.9 ± 5.5%, respectively). At 1,000 and 2,000 m depths, where HS concentrations were the highest (>350 µM), the proportion of hgcA genes from Verrucomicrobiota and UDesulfacyla decreased, while those from other Desulfobacterota and Chloroflexota remained dominant (Fig. 5B; Data Sheet S1B). Also, hgcA genes from Firmicutes represented 1.4%–6.7% of all reads at the SOL-AOL transition (110–130 m), while they were undetected in all the other sampled depths (Data Sheet S1B and D).

Relationships between environmental gradients, Hg-related variables, and microbial stratification over depth

PCoA analyses showed that the structure of both the 16S rRNA gene-based prokaryotic community (Fig. 3A) and hgc+ microbial groups (Fig. 3B) clustered similarly with depth (PERMANOVA, P < 0.05), according to the three redox zones (OL, SOL, and AOL). This microbial stratification over depth can be related to the observed geochemical gradients of oxygen, HS, and MeHg concentrations, along with other stratified parameters (Table 1).

For the MEDBlack samples , the qPCR-estimated abundances of hgcA genes from Desulfobacterota, Firmicutes, and Archaea-Chloroflexota were significantly positively correlated with MeHg and HS concentrations, and negatively correlated with oxygen concentrations (Spearman rank correlations, P-value <0.01; Fig. 3C). Several other environmental parameters also appeared to be stratified and co-varied with oxygen along depth (Table 1).

For station 2 studied in the Phoxy cruise, the correlations between the MG-estimated abundance of hgcA genes and environmental conditions depended on the microbial groups (Fig. 3C). The abundances of hgcA genes from Bacteroidota and Verrucomicrobiota significantly increased with oxygen depletion but were not significantly correlated to HS concentrations. In contrast, hgc+ Chloroflexota, KSB1 Candidate Division, and Planctomycetota were positively correlated to HS concentrations and not significantly related to oxygen concentrations. Finally, hgcA genes from Desulfobacterota were negatively correlated to oxygen concentrations and positively correlated to HS concentrations (Fig. 3C). The hgc+ community clustering in the AOL was characterized by discriminant hgcA genes affiliated to Desulfobacterota (UDesulfatibia), Chloroflexota (Anaerolineales), and Planctomycetota (mainly from Phycisphaerae), while the hgc+ community in the SOL was discriminated by hgcA genes affiliated to Kiritimatiellales, UDesulfacyla, Bacteroidales, Desulfobacterales, and other PVC (Planctomycetota, Verrucomicrobiota, and Chlamydiota) superphylum members (lefse analysis , P < 0.05, Fig. S4), thus confirming the oxygen-dependent niche partitioning of potential methylators at a fine taxonomic resolution.

DISCUSSION

Coupling methodological approaches to identify bioindicators of Hg methylation in the environment

Our 16S rRNA gene metabarcoding data support previous studies that reported the enrichment of Desulfobacterota, Planctomycetota, Acidobacteriota, and Firmicutes with increasing depth, and the restriction of Nitrospirota, Chloroflexota, and Verrucomicrobiota to the anoxic waters of the Black Sea (28, 41). Several of the dominant microbial lineages found in and below the redoxcline include hgc+ microorganisms. However, studies based on 16S rRNA gene taxonomic classification are often not sufficient to predict the occurrence of Hg methylators, since Hg methylation is a species- (and possibly strain-) specific trait (3). Alternative approaches targeting the hgc genes as a biomarker of microbial Hg methylation have been proposed (37, 42, 43). To avoid the biases due to the large polyphyletic diversity of the hgcA gene (9), and the overrepresentation of hgcA sequences from Desulfobacterota in databases of known Hg methylators used for primer design (8, 43), clade-specific qPCR primers have been developed, targeting hgcA genes from each of the three dominant Hg-methylating clades, i.e., Desulfobacterota, Archaea, and Firmicutes (37). This approach yielded results similar to metagenome-derived estimates for the identification of Hg methylation biomarkers (42), and is preferable to detect taxa-dependent correlations with environmental and/or functional outcomes. It is important to highlight that the outcomes of different methods should be interpreted cautiously since some discrepancies have been previously reported between, e.g., metagenomics, functional gene sequencing, cloning, qPCR, and 16S metabarcoding (14, 42, 44). Finally, DNA-based approaches should be complemented by gene expression and methylation rates measurements in order to confirm the involvement of potential Hg methylators.

Geochemical and microbial homogeneity along the Black Sea transect

Here, although qPCR and metagenomic estimates have been applied to samples from two different cruises, the results of the two cruises yield comparable results, including (i) similar stratification pattern of hgcA abundance across water depth and environmental conditions, and (ii) similar taxonomic identification and abundance distribution of putative Hg methylators. Even if metagenomic analysis has been carried out only at station 2 during the Phoxy cruise, our results are likely representative for the basin as a whole because of the high horizontal homogeneity of the Black Sea (excluding coastal areas), in terms of microbial community structure (as shown in the present and previous studies) (26) hydrography (27) and geochemistry (25). Here, all the microbial indicators and metrics (i.e., total abundances, abundance of hgcA-carriers from different clades, alpha diversity, community structure, and composition) were similar across the east-west transect, as well as the full-depth high-resolution Hg and MeHg concentration profiles. Significant positive correlations were observed between hgcA qPCR estimates from the three targeted microbial groups (i.e., Desulfobacterota, Firmicutes, and Archaea-Chloroflexota) and MeHg concentrations. Such correlative links between hgcA (gene or transcript) abundance and MeHg concentration and/or formation activity have been previously reported (19, 45, 46), but are not always observed, depending on the ecosystems (47, 48), as documented also for other metabolic processes (49).

A diverse community of hgc+ microorganisms is distributed along the redox gradient in the Black Sea

We demonstrate that not only the overall community but also the abundance and diversity of hgc+ microorganisms vary with the redox gradient in the water column of the Black Sea. The very low proportion of hgc genes detected in the oxic layer (and their taxonomic affiliation) is further discussed in Supplemental Information 3.1. Our findings showing a strong relation between oxygen depletion and hgc+ microorganism abundance are in line with previous studies in marine, brackish, and freshwater environments (15, 17 - 19). We provide the first evidence for microbial potential to produce MeHg in the anoxic sulfidic waters of the Black Sea, as previously suggested by a modeling approach based on geochemical data (25). This disagrees with earlier studies where persistently high sulfide concentrations were believed to inhibit Hg methylation in the AOL of the Black Sea (24) and other systems (50, 51). Similar to our results, maximal methylation activity was also reported under sulfidic conditions in stratified brackish water (19) and a meromictic lake (52). The dual role of sulfide in Hg methylation is complex and still uncertain (51, 53).

Desulfobacterota members exhibit the highest diversity and abundances of hgcA genes in the Black Sea water column. The presence of Desulfobacterota in the anoxic water layer of the Black Sea can be explained by their metabolisms as sulfate reducers, iron reducers, and/or fermentative syntrophic in oxygen-deficient environments (54). Sulfate reduction has been previously reported in the Black Sea anoxic water (30, 55) and is also supported by our high HS concentrations in the AOL. For decades, Desulfobacterota members have been confirmed to be capable of Hg methylation and/or carrying hgc genes (3, 11). Desulfobacterota have also previously been identified as prevalent hgc+ microorganisms in many anoxic marine waters (17 - 19) and sediments (13, 56). In our work, certain hgcA genes belong to MAGs previously reconstructed from the Phoxy metagenomes (30). Among them, the hgc+ MAGs UDesulfatibia profunda NIOZ-UU30 and UDesulfacyla NIOZ-UU19, enriched in the anoxic waters, were described as probably having a strict sulfate-reducing lifestyle. By contrast, the hgc+ sulfate reducers UDesulfacyla euxinica NIOZ-UU27,UDesulfatibia vada NIOZ-UU17, and UDesulfobacula maris NIOZ-UU16, which were abundant in the suboxic waters and dominant at the top of the anoxic waters, feature a more flexible potential metabolism, with the ability to gain energy from the reduction of diverse electron acceptors (S0, thiosulfate, tetrathionate, nitrate, nitrite), possibly including oxygen respiration (30). The MAG of the SRB UDesulfobia pelagia NIOZ-UU47, for which hgcA genes were found between 105 and 250 m, seems to have the ability to fix nitrogen. Altogether, these results show that Desulfobacterota-mediated MeHg formation in the Black Sea may be coupled to sulfate reduction but also to other metabolic pathways depending on the redox niche.

Certain Anaerolineales (Chloroflexota) are also part of the dominant hgcA-carriers in the suboxic and anoxic waters of the Black Sea including the MAGs NIOZ-UU11 and NIOZ-UU52. Anaerolineales are fermenters, in possible syntrophic association with methanogens (57). Anaerolineales MAGs were previously identified as highly abundant in the Black Sea, where some of them carried sulfate reduction genes (28). Although there is still limited genomic information about members of this group, a hgc+ MAG Anaerolineales representative (BSW_bin111) was detected in the anoxic brackish water of the Baltic Sea (19). In addition, Phycisphaerae (Planctomycetota), Kiritimatiellales (Verrucomicrobiota), and Bacteroidales (Bacteroidota) were identified as major potential Hg methylators in the oxygen-deficient waters of the Black Sea. Among these new, underappreciated, fermentative hgcA carriers, the Bacteroidota MAG NIOZ-UU65 was equipped with polysulfide reductase genes (30). Phycisphaerales have been identified in the euxinic waters of the Cariaco basin as attached to particles (58) and in the Black Sea (59) as potential degraders of newly formed OM not linked to the redox gradient (60), and some type strains seemed capable of nitrate reduction (61). Phycisphaerales have been reported as minor putative Hg methylator in marine sediments (13), salt marsh, and freshwater sediment (43). Culture and single-cell genomics of Kiritimatiellales representatives indicated a fermentative lifestyle, with the capacity for degradation of complex and recalcitrant polysaccharides and glycoproteins, as well as hydrolysis of sulfate esters, with wide oxygen and salinity tolerance, and a preference for biofilm habitats (62 - 65). Kiritimatiellales were previously identified by metagenomic approaches among the most prominent putative Hg methylators in sediment and anoxic water of eutrophic sulfate-rich freshwater lakes (14, 15) and in the anoxic brackish water of the Baltic Sea (19). Overall, fermenters from Anaerolineales, Phycisphaerae, Kiritimatiellales, and Bacteroidales have been rarely reported as putative Hg methylators, usually at low abundance in ecosystems different from the present one. To our knowledge, this is the first report of their substantial joint contribution to Hg methylation, conforming a unique assemblage in a permanently stratified marine ecosystem. Among these diverse Hg methylators candidates found in the Black Sea suboxic/anoxic waters, some lineages (Anaerolineales and Kiritimatiellales) are common to other euxinic basins (17, 19), suggesting that they may be part of the important mediators of Hg methylation in permanently or not permanently anoxic water from marine and/or brackish environments with high sulfide concentrations. However, it is unclear if this diversity is a common trait of (not euxinic) OMZ, where Hg methylators have been rarely detected (10). Further studies should compare the hgc+ MAGs identified here and in similar oxygen-depleted marine systems, to explore the metabolic versatility of Hg-methylating microorganisms and their environmental drivers.

Finally, our results suggest that the qPCR estimates of hgcA genes identified by primers primarily designed to target Archaea are overestimated. This is supported by cloning-sequencing of PCR products obtained using Archaea-specific hgcA qPCR primers, showing that some amplicon sequences group with Chloroflexota rather than Archaea (Supplemental Information 1.4, Fig. S2). Additionally, our metagenome analyses consistently show that hgc+ Chloroflexota are major putative Hg methylation contributors, especially in the AOL, while Archaea-assigned hgcA are rare and not abundant (Data Sheet S1B and D). Recently, an analysis of publicly available MAGs revealed high similarities of hgc genes from Euryarchaeota and Chloroflexota, potentially due to horizontal gene transfers (9). Altogether, these results suggest that the Archaea-hgcA primers from Christensen et al. (37) are less specific than initially thought and likely include hgcA genes from other clades such as Chloroflexota.

Conclusion

Oxygen-limited and anoxic areas are spreading in the coastal and offshore ocean, implying modifications of biogeochemical cycles. The Black Sea offers a unique opportunity to study the effect of oxygen gradients on biogeochemical cycles such as Hg transformations. Our findings highlight that a unique combination of diverse dominant hgc+ microbes can coexist and jointly contribute to MeHg production in marine environments, with niche partitioning according to the redox gradient. We identified members of Desulfobacterota, Chloroflexota, Verrucomicrobiota, Planctomycetota, and Bacteroidota as the main actors of Hg methylation in the Black Sea water column. The microbial communities, including putative Hg methylators, were horizontally homogeneous across the Black Sea, but vertically stratified. The abundance of hgcA genes increased with depth, being positively correlated with MeHg concentration and negatively with oxygen concentration. Our DNA-based results support that Hg methylation potentially occurs predominantly in the anoxic waters of the Black Sea, which should be further confirmed by measuring gene expression and/or methylation rates. Microorganisms harboring hgc+ were dominated by Desulfobacterota, followed by a high diversity of previously less recognized Hg methylators belonging to Phycisphaerae, Kiritimatiellales, and Anaerolineales. The strong environmental gradients across the Black Sea water column affect the microbial community composition, resulting in a partitioning of Hg-methylating microorganisms, and their associated metabolic pathways, differing across redox niches. Our results, robustly validated by two different methodological approaches (qPCR and metagenomics), were consistent with measured environmental parameters, including MeHg concentration. By identifying marine anoxic niches as a primary MeHg source, this study is of major relevance in the context of global warming and anthropogenic activity which currently result in enhanced seawater deoxygenation and global expansion of anoxic zones.

ACKNOWLEDGMENTS

This study was financially supported by the French National Research Institute for Sustainable Development (IRD) through the M.I.O. internal grant “ACTION SUD-Commet” (L. Cabrol), the Severo Ochoa Excellence Program postdoctoral fellowship awarded in 2021 to Eric Capo (CEX2019-000928-S), and the Ramón y Cajal program (RYC2019-028400-I, AEI Spain) awarded to Andrea G. Bravo. We acknowledge the Dutch funding agency (project number: 822.01.015) of the national science foundation NWO for funding this work as part of GEOTRACES. L.-E.H.-B.'s work was supported by research grant ERC-2010-StG_20091028 from the European Research Council.

We thank the chief scientists of the MEDBlack cruise, M. J. A. Rijkenberg, L. J. A. Gerringa, and the shipboard party for their support. A special thanks goes to Matthew Patey for handling the in situ pumps. We thank Sophie Guasco at the M.I.O. for technical support with cloning sequencing of hgcA genes. The computations were performed on resources provided by the Swedish Research Council (grants to S.B.) and SNIC through Uppsala Multidisciplinary Center for Advanced Computational Science (UPPMAX) using the compute project SNIC 2021/5-53.

The authors have no competing interests to declare.

Contributor Information

Léa Cabrol, Email: lea.cabrol@mio.osupytheas.fr.

Eric Capo, Email: eric.capo@umu.se.

Michael S. Rappe, University of Hawaii at Manoa, Kaneohe, Hawaii, USA

DATA AVAILABILITY

Raw sequences have been deposited at NCBI GenBank, SRA database, under the BioProject accession number PRJNA895066.

SUPPLEMENTAL MATERIAL

The following material is available online at https://doi.org/10.1128/msystems.00537-23.

Supplemental Information. msystems.00537-23-s0001.docx.

Table S1, supplemental text, and Figure S1 to S4.

DOI: 10.1128/msystems.00537-23.SuF1
Data Sheet. msystems.00537-23-s0002.xlsx.

Environmental and molecular data from both cruises, OTU abundance table and taxonomy, hgcA and hgcB genes found in Phoxy cruise metagenomes, and community composition.

DOI: 10.1128/msystems.00537-23.SuF2

ASM does not own the copyrights to Supplemental Material that may be linked to, or accessed through, an article. The authors have granted ASM a non-exclusive, world-wide license to publish the Supplemental Material files. Please contact the corresponding author directly for reuse.

REFERENCES

  • 1. Outridge PM, Mason RP, Wang F, Guerrero S, Heimbürger-Boavida LE. 2018. Updated global and oceanic mercury budgets for the United Nations global mercury assessment 2018. Environ Sci Technol 52:11466–11477. doi: 10.1021/acs.est.8b01246 [DOI] [PubMed] [Google Scholar]
  • 2. Zhang Y, Song Z, Huang S, Zhang P, Peng Y, Wu P, Gu J, Dutkiewicz S, Zhang H, Wu S, Wang F, Chen L, Wang S, Li P. 2021. Global health effects of future atmospheric mercury emissions. Nat Commun 12:3035. doi: 10.1038/s41467-021-23391-7 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3. Bravo AG, Cosio C. 2020. Biotic formation of methylmercury: a bio-physico-chemical conundrum. Limnol Oceanogr 65:1010–1027. doi: 10.1002/lno.11366 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4. Heimbürger L-E, Cossa D, Marty J-C, Migon C, Averty B, Dufour A, Ras J. 2010. Methyl mercury distributions in relation to the presence of nano- and picophytoplankton in an oceanic water column (Ligurian Sea, North-Western Mediterranean). Geochim Cosmochim Acta 74:5549–5559. doi: 10.1016/j.gca.2010.06.036 [DOI] [Google Scholar]
  • 5. Soerensen AL, Schartup AT, Skrobonja A, Bouchet S, Amouroux D, Liem-Nguyen V, Björn E. 2018. Deciphering the role of water column redoxclines on methylmercury cycling using speciation modeling and observations from the Baltic Sea. Global Biogeochem Cycles 32:1498–1513. doi: 10.1029/2018GB005942 [DOI] [Google Scholar]
  • 6. Yu R-Q, Barkay T. 2022. Microbial mercury transformations: molecules, functions and organisms. Adv Appl Microbiol 118:31–90. doi: 10.1016/bs.aambs.2022.03.001 [DOI] [PubMed] [Google Scholar]
  • 7. Parks JM, Johs A, Podar M, Bridou R, Hurt RA, Smith SD, Tomanicek SJ, Qian Y, Brown SD, Brandt CC, Palumbo AV, Smith JC, Wall JD, Elias DA, Liang L. 2013. The genetic basis for bacterial mercury methylation. Science 339:1332–1335. doi: 10.1126/science.1230667 [DOI] [PubMed] [Google Scholar]
  • 8. Capo E, Peterson BD, Kim M, Jones DS, Acinas SG, Amyot M, Bertilsson S, Björn E, Buck M, Cosio C, Elias DA, Gilmour C, Goñi-Urriza M, Gu B, Lin H, Liu Y-R, McMahon K, Moreau JW, Pinhassi J, Podar M, Puente-Sánchez F, Sánchez P, Storck V, Tada Y, Vigneron A, Walsh DA, Vandewalle-Capo M, Bravo AG, Gionfriddo CM. 2023. A consensus protocol for the recovery of mercury methylation genes from metagenomes. Mol Ecol Resour 23:190–204. doi: 10.1111/1755-0998.13687 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9. McDaniel EA, Peterson BD, Stevens SLR, Tran PQ, Anantharaman K, McMahon KD. 2020. Expanded phylogenetic diversity and metabolic flexibility of mercury-methylating microorganisms. mSystems 5:e00299-20. doi: 10.1128/mSystems.00299-20 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 10. Podar M, Gilmour CC, Brandt CC, Soren A, Brown SD, Crable BR, Palumbo AV, Somenahally AC, Elias DA. 2015. Global prevalence and distribution of genes and microorganisms involved in mercury methylation. Sci Adv 1:e1500675. doi: 10.1126/sciadv.1500675 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11. Gilmour CC, Podar M, Bullock AL, Graham AM, Brown SD, Somenahally AC, Johs A, Hurt RA, Bailey KL, Elias DA. 2013. Mercury methylation by novel microorganisms from new environments. Environ Sci Technol 47:11810–11820. doi: 10.1021/es403075t [DOI] [PubMed] [Google Scholar]
  • 12. Gilmour CC, Bullock AL, McBurney A, Podar M, Elias DA. 2018. Robust mercury methylation across diverse methanogenic Archaea. mBio 9:e02403-17. doi: 10.1128/mBio.02403-17 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13. Capo E, Broman E, Bonaglia S, Bravo AG, Bertilsson S, Soerensen AL, Pinhassi J, Lundin D, Buck M, Hall POJ, Nascimento FJA, Björn E. 2022. Oxygen-deficient water zones in the Baltic Sea promote uncharacterized Hg methylating microorganisms in underlying sediments. Limnology & Oceanography 67:135–146. doi: 10.1002/lno.11981 [DOI] [Google Scholar]
  • 14. Jones DS, Walker GM, Johnson NW, Mitchell CPJ, Coleman Wasik JK, Bailey JV. 2019. Molecular evidence for novel mercury methylating microorganisms in sulfate-impacted lakes. ISME J 13:1659–1675. doi: 10.1038/s41396-019-0376-1 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15. Peterson BD, McDaniel EA, Schmidt AG, Lepak RF, Janssen SE, Tran PQ, Marick RA, Ogorek JM, DeWild JF, Krabbenhoft DP, McMahon KD. 2020. Mercury methylation genes identified across diverse anaerobic microbial guilds in a eutrophic sulfate-enriched lake. Environ Sci Technol 54:15840–15851. doi: 10.1021/acs.est.0c05435 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16. Vigneron A, Cruaud P, Aubé J, Guyoneaud R, Goñi-Urriza M. 2021. Transcriptomic evidence for versatile metabolic activities of mercury cycling microorganisms in brackish microbial mats. NPJ Biofilms Microbiomes 7:83. doi: 10.1038/s41522-021-00255-y [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17. Lin H, Ascher DB, Myung Y, Lamborg CH, Hallam SJ, Gionfriddo CM, Holt KE, Moreau JW. 2021. Mercury methylation by metabolically versatile and cosmopolitan marine bacteria. ISME J 15:1810–1825. doi: 10.1038/s41396-020-00889-4 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18. Capo E, Bravo AG, Soerensen AL, Bertilsson S, Pinhassi J, Feng C, Andersson AF, Buck M, Björn E. 2020. Deltaproteobacteria and spirochaetes-like bacteria are abundant putative mercury methylators in oxygen-deficient water and marine particles in the Baltic sea. Front Microbiol 11:574080. doi: 10.3389/fmicb.2020.574080 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19. Capo E, Feng C, Bravo AG, Bertilsson S, Soerensen AL, Pinhassi J, Buck M, Karlsson C, Hawkes J, Björn E. 2022. Expression levels of hgcAB genes and mercury availability jointly explain methylmercury formation in stratified brackish waters. Environ Sci Technol 56:13119–13130. doi: 10.1021/acs.est.2c03784 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20. Breitburg D, Levin LA, Oschlies A, Grégoire M, Chavez FP, Conley DJ, Garçon V, Gilbert D, Gutiérrez D, Isensee K, Jacinto GS, Limburg KE, Montes I, Naqvi SWA, Pitcher GC, Rabalais NN, Roman MR, Rose KA, Seibel BA, Telszewski M, Yasuhara M, Zhang J. 2018. Declining oxygen in the global ocean and coastal waters. Science 359:1–11. doi: 10.1126/science.aam7240 [DOI] [PubMed] [Google Scholar]
  • 21. Wakeham SG. 2020. Organic biogeochemistry in the oxygen-deficient ocean: a review. Organic Geochemistry 149:104096. doi: 10.1016/j.orggeochem.2020.104096 [DOI] [Google Scholar]
  • 22. Jürgens K, Taylor GT. 2018. Microbial ecology and biogeochemistry of oxygen-deficient water columns, p 231–288. In Gasol J, Kirchman D (ed), Microbial ecology of the oceans. John Wiley & Sons, Inc. [Google Scholar]
  • 23. Glazer BT, Luther GW, Konovalov SK, Friederich GE, Trouwborst RE, Romanov AS. 2006. Spatial and temporal variability of the Black Sea suboxic zone. Deep-Sea Res II: Top Stud Oceanogr 53:1756–1768. doi: 10.1016/j.dsr2.2006.03.022 [DOI] [Google Scholar]
  • 24. Lamborg CH, Yiğiterhan O, Fitzgerald WF, Balcom PH, Hammerschmidt CR, Murray J. 2008. Vertical distribution of mercury species at two sites in the Western Black Sea. Marine Chemistry 111:77–89. doi: 10.1016/j.marchem.2007.01.011 [DOI] [Google Scholar]
  • 25. Rosati G, Heimbürger LE, Melaku Canu D, Lagane C, Laffont L, Rijkenberg MJA, Gerringa LJA, Solidoro C, Gencarelli CN, Hedgecock IM, De Baar HJW, Sonke JE. 2018. Mercury in the Black Sea: new insights from measurements and numerical modeling. Global Biogeochem Cycles 32:529–550. doi: 10.1002/2017GB005700 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26. Zhang Y, Pavlovska M, Stoica E, Prekrasna I, Yang J, Slobodnik J, Zhang X, Dykyi E. 2020. Holistic pelagic biodiversity monitoring of the Black Sea via eDNA metabarcoding approach: from bacteria to marine mammals. Environ Int 135:105307. doi: 10.1016/j.envint.2019.105307 [DOI] [PubMed] [Google Scholar]
  • 27. Zatsepin AG. 2003. Observations of Black Sea mesoscale eddies and associated horizontal mixing. J Geophys Res 108:1–27. doi: 10.1029/2002JC001390 [DOI] [Google Scholar]
  • 28. Cabello-Yeves PJ, Callieri C, Picazo A, Mehrshad M, Haro-Moreno JM, Roda-Garcia JJ, Dzhembekova N, Slabakova V, Slabakova N, Moncheva S, Rodriguez-Valera F. 2021. The microbiome of the Black Sea water column analyzed by shotgun and genome centric metagenomics. Environ Microbiome 16:5. doi: 10.1186/s40793-021-00374-1 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 29. Suominen S, Dombrowski N, Sinninghe Damsté JS, Villanueva L. 2021. A diverse uncultivated microbial community is responsible for organic matter degradation in the Black Sea sulphidic zone. Environ Microbiol 23:2709–2728. doi: 10.1111/1462-2920.14902 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30. van Vliet DM, von Meijenfeldt FAB, Dutilh BE, Villanueva L, Sinninghe Damsté JS, Stams AJM, Sánchez-Andrea I. 2021. The bacterial sulfur cycle in expanding dysoxic and euxinic marine waters. Environ Microbiol 23:2834–2857. doi: 10.1111/1462-2920.15265 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 31. Villanueva L, von Meijenfeldt FAB, Westbye AB, Yadav S, Hopmans EC, Dutilh BE, Damsté JSS. 2021. Bridging the membrane lipid divide: bacteria of the FCB group superphylum have the potential to synthesize archaeal ether lipids. ISME J 15:168–182. doi: 10.1038/s41396-020-00772-2 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 32. Stewart K, Kassakian S, Krynytzky M, DiJulio D, Murray JW. 2007. Oxic, Suboxic, and Anoxic conditions in the black sea, p 1–22. In Yanko-Hombach V, Gilbert AS, Panin N, Dolukhanov P (ed), The Black Sea flood question: changes in coastline, climate, and settlement human. Springer. doi: 10.1007/978-1-4020-5302-3 [DOI] [Google Scholar]
  • 33. Sollai M, Villanueva L, Hopmans EC, Reichart G-J, Sinninghe Damsté JS. 2019. A combined lipidomic and 16S rRNA gene amplicon sequencing approach reveals archaeal sources of intact polar lipids in the stratified Black Sea water column. Geobiology 17:91–109. doi: 10.1111/gbi.12316 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 34. Wang Y, Qian P-Y, Field D. 2009. Conservative fragments in bacterial 16S rRNA genes and primer design for 16S ribosomal DNA amplicons in metagenomic studies. PLoS ONE 4:e7401. doi: 10.1371/journal.pone.0007401 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 35. Schwob G, Cabrol L, Poulin E, Orlando J. 2020. Characterization of the gut microbiota of the antarctic heart urchin (spatangoida) Abatus agassizii. Front Microbiol 11:308. doi: 10.3389/fmicb.2020.00308 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 36. Mahé F, Czech L, Stamatakis A, Quince C, de Vargas C, Dunthorn M, Rognes T. 2021. Swarm v3: towards tera-scale amplicon clustering. Bioinformatics 38:267–269. doi: 10.1093/bioinformatics/btab493 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 37. Christensen GA, Wymore AM, King AJ, Podar M, Hurt RA, Santillan EU, Soren A, Brandt CC, Brown SD, Palumbo AV, Wall JD, Gilmour CC, Elias DA. 2016. Development and validation of broad-range qualitative and clade-specific quantitative molecular probes for assessing mercury methylation in the environment. Appl Environ Microbiol 82:6068–6078. doi: 10.1128/AEM.01271-16 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 38. Gionfriddo CM, Capo E, Peterson B, Lin H, Jones D, Bravo AG, Bertilsson S, Moreau J, McMahon K, Elias D, Gilmour C. 2021. Hg-MATE-dB.V1.01142021. Hg-Cycling Microorg. Aquat Terr Ecosyst database. doi: 10.25573/serc.13105370 [DOI] [Google Scholar]
  • 39. Finn RD, Clements J, Eddy SR. 2011. HMMER web server: interactive sequence similarity searching. Nucleic Acids Res 39:W29–W37. doi: 10.1093/nar/gkr367 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 40. Matsen FA, Kodner RB, Armbrust EV. 2010. Pplacer: linear time maximum-likelihood and Bayesian phylogenetic placement of sequences onto a fixed reference tree. BMC Bioinformatics 11:538. doi: 10.1186/1471-2105-11-538 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 41. Ozturk RC, Altinok I, Feyzioglu AM, Capkin E, Yildiz I. 2021. Influence of the depth and season on microbial community dynamics of the black sea. Res sq. doi: 10.21203/rs.3.rs-693853/v1 [DOI]
  • 42. Christensen GA, Gionfriddo CM, King AJ, Moberly JG, Miller CL, Somenahally AC, Callister SJ, Brewer H, Podar M, Brown SD, Palumbo AV, Brandt CC, Wymore AM, Brooks SC, Hwang C, Fields MW, Wall JD, Gilmour CC, Elias DA. 2019. Determining the reliability of measuring mercury cycling gene abundance with correlations with mercury and methylmercury concentrations. Environ Sci Technol 53:8649–8663. doi: 10.1021/acs.est.8b06389 [DOI] [PubMed] [Google Scholar]
  • 43. Gionfriddo CM, Wymore AM, Jones DS, Wilpiszeski RL, Lynes MM, Christensen GA, Soren A, Gilmour CC, Podar M, Elias DA. 2020. An improved hgcAB primer set and direct high-throughput sequencing expand Hg-methylator diversity in nature. Front Microbiol 11:541554. doi: 10.3389/fmicb.2020.541554 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 44. Roth S, Poulin BA, Baumann Z, Liu X, Zhang L, Krabbenhoft DP, Hines ME, Schaefer JK, Barkay T. 2021. Nutrient inputs stimulate mercury methylation by syntrophs in a subarctic peatland. Front Microbiol 12:741523. doi: 10.3389/fmicb.2021.741523 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 45. Vishnivetskaya TA, Hu H, Van Nostrand JD, Wymore AM, Xu X, Qiu G, Feng X, Zhou J, Brown SD, Brandt CC, Podar M, Gu B, Elias DA. 2018. Microbial community structure with trends in methylation gene diversity and abundance in mercury-contaminated rice paddy soils in Guizhou, China. Environ Sci Process Impacts 20:673–685. doi: 10.1039/c7em00558j [DOI] [PubMed] [Google Scholar]
  • 46. Peterson BD, Krabbenhoft DP, McMahon KD, Ogorek JM, Tate MT, Orem WH, Poulin BA. 2023. Environmental formation of methylmercury is controlled by synergy of inorganic mercury bioavailability and microbial mercury-methylation capacity. Environ Microbiol:1–15. doi: 10.1111/1462-2920.16364 [DOI] [PubMed] [Google Scholar]
  • 47. Bravo AG, Loizeau J-L, Dranguet P, Makri S, Björn E, Ungureanu VG, Slaveykova VI, Cosio C. 2016. Persistent Hg contamination and occurrence of Hg-methylating transcript (hgcA) downstream of a chlor-alkali plant in the Olt River (Romania). Environ Sci Pollut Res Int 23:10529–10541. doi: 10.1007/s11356-015-5906-4 [DOI] [PubMed] [Google Scholar]
  • 48. Christensen GA, Somenahally AC, Moberly JG, Miller CM, King AJ, Gilmour CC, Brown SD, Podar M, Brandt CC, Brooks SC, Palumbo AV, Wall JD, Elias DA. 2018. Carbon amendments alter microbial community structure and net mercury methylation potential in sediments. Appl Environ Microbiol 84:e01049-17. doi: 10.1128/AEM.01049-17 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 49. Rocca JD, Hall EK, Lennon JT, Evans SE, Waldrop MP, Cotner JB, Nemergut DR, Graham EB, Wallenstein MD. 2015. Relationships between protein-encoding gene abundance and corresponding process are commonly assumed yet rarely observed. ISME J 9:1693–1699. doi: 10.1038/ismej.2014.252 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 50. Benoit JM, Gilmour CC, Mason RP, Heyes A. 1999. Sulfide controls on mercury speciation and bioavailability to methylating bacteria in sediment pore waters. Environ Sci Technol 33:951–957. doi: 10.1021/es9808200 [DOI] [Google Scholar]
  • 51. Hsu-Kim H, Kucharzyk KH, Zhang T, Deshusses MA. 2013. Mechanisms regulating mercury bioavailability for methylating microorganisms in the aquatic environment: a critical review. Environ Sci Technol 47:2441–2456. doi: 10.1021/es304370g [DOI] [PubMed] [Google Scholar]
  • 52. Tisserand D, Guédron S, Viollier E, Jézéquel D, Rigaud S, Campillo S, Sarret G, Charlet L, Cossa D. 2022. Mercury, organic matter, iron, and sulfur co-cycling in a ferruginous meromictic lake. Appl Geochem 146:105463. doi: 10.1016/j.apgeochem.2022.105463 [DOI] [Google Scholar]
  • 53. Regnell O, Watras CJ. 2019. Microbial mercury methylation in aquatic environments: a critical review of published field and laboratory studies. Environ Sci Technol 53:4–19. doi: 10.1021/acs.est.8b02709 [DOI] [PubMed] [Google Scholar]
  • 54. Waite DW, Chuvochina M, Pelikan C, Parks DH, Yilmaz P, Wagner M, Loy A, Naganuma T, Nakai R, Whitman WB, Hahn MW, Kuever J, Hugenholtz P. 2020. Proposal to reclassify the proteobacterial classes Deltaproteobacteria and Oligoflexia, and the phylum Thermodesulfobacteria into four phyla reflecting major functional capabilities. Int J Syst Evol Microbiol 70:5972–6016. doi: 10.1099/ijsem.0.004213 [DOI] [PubMed] [Google Scholar]
  • 55. Neretin LN, Volkov II, Böttcher ME, Grinenko VA. 2001. A sulfur budget for the black sea anoxic zone. Deep-Sea Res I: Oceanogr Res Pap 48:2569–2593. doi: 10.1016/S0967-0637(01)00030-9 [DOI] [Google Scholar]
  • 56. Azaroff A, Goñi Urriza M, Gassie C, Monperrus M, Guyoneaud R. 2020. Marine mercury-methylating microbial communities from coastal to Capbreton Canyon sediments (North Atlantic ocean). Environ Pollut 262:114333. doi: 10.1016/j.envpol.2020.114333 [DOI] [PubMed] [Google Scholar]
  • 57. Sekiguchi Y, Yamada T, Hanada S, Ohashi A, Harada H, Kamagata Y. 2003. Anaerolinea thermophila gen. nov., sp. nov. and Caldilinea aerophila gen. nov., sp. nov., novel filamentous thermophiles that represent a previously uncultured lineage of the domain Bacteria at the subphylum level. Int J Syst Evol Microbiol 53:1843–1851. doi: 10.1099/ijs.0.02699-0 [DOI] [PubMed] [Google Scholar]
  • 58. Suter EA, Pachiadaki M, Taylor GT, Astor Y, Edgcomb VP. 2018. Free-living chemoautotrophic and particle-attached heterotrophic prokaryotes dominate microbial assemblages along a pelagic redox gradient. Environ Microbiol 20:693–712. doi: 10.1111/1462-2920.13997 [DOI] [PubMed] [Google Scholar]
  • 59. Fuchsman CA, Staley JT, Oakley BB, Kirkpatrick JB, Murray JW. 2012. Free-living and aggregate-associated planctomycetes in the black sea. FEMS Microbiol Ecol 80:402–416. doi: 10.1111/j.1574-6941.2012.01306.x [DOI] [PubMed] [Google Scholar]
  • 60. Suominen S, Gomez‐Saez GV, Dittmar T, Sinninghe Damsté JS, Villanueva L. 2022. Interplay between microbial community composition and chemodiversity of dissolved organic matter throughout the black sea water column redox gradient. Limnology & Oceanography 67:329–347. doi: 10.1002/lno.11995 [DOI] [Google Scholar]
  • 61. Fukunaga Y, Kurahashi M, Sakiyama Y, Ohuchi M, Yokota A, Harayama S. 2009. Phycisphaera mikurensis gen. nov., sp. nov., isolated from a marine alga, and proposal of Phycisphaeraceae fam. nov., Phycisphaerales ord. nov. and Phycisphaerae classis nov. in the phylum Planctomycetes. J Gen Appl Microbiol 55:267–275. doi: 10.2323/jgam.55.267 [DOI] [PubMed] [Google Scholar]
  • 62. Sackett JD, Kruger BR, Becraft ED, Jarett JK, Stepanauskas R, Woyke T, Moser DP. 2019. Four draft single-cell genome sequences of novel, nearly identical Kiritimatiellaeota strains isolated from the continental deep subsurface. Microbiol Resour Announc 8:e01249-18. doi: 10.1128/MRA.01249-18 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 63. Spring S, Bunk B, Spröer C, Schumann P, Rohde M, Tindall BJ, Klenk H-P. 2016. Characterization of the first cultured representative of Verrucomicrobia subdivision 5 indicates the proposal of a novel phylum. ISME J 10:2801–2816. doi: 10.1038/ismej.2016.84 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 64. van Vliet DM, Lin Y, Bale NJ, Koenen M, Villanueva L, Stams AJM, Sánchez-Andrea I. 2020. Pontiella desulfatans gen. nov., sp. nov., and pontiella sulfatireligans sp. nov., two marine anaerobes of the pontiellaceae fam. nov. producing sulfated glycosaminoglycan-like exopolymers. Microorganisms 8:1–22. doi: 10.3390/microorganisms8060920 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 65. van Vliet DM, Palakawong Na Ayudthaya S, Diop S, Villanueva L, Stams AJM, Sánchez-Andrea I. 2019. Anaerobic degradation of sulfated polysaccharides by two novel Kiritimatiellales strains isolated from black sea sediment. Front Microbiol 10:253. doi: 10.3389/fmicb.2019.00253 [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Supplemental Information. msystems.00537-23-s0001.docx.

Table S1, supplemental text, and Figure S1 to S4.

DOI: 10.1128/msystems.00537-23.SuF1
Data Sheet. msystems.00537-23-s0002.xlsx.

Environmental and molecular data from both cruises, OTU abundance table and taxonomy, hgcA and hgcB genes found in Phoxy cruise metagenomes, and community composition.

DOI: 10.1128/msystems.00537-23.SuF2

Data Availability Statement

Raw sequences have been deposited at NCBI GenBank, SRA database, under the BioProject accession number PRJNA895066.


Articles from mSystems are provided here courtesy of American Society for Microbiology (ASM)

RESOURCES