ABSTRACT
Methanethiol (MT) is a sulfur-containing compound produced during dimethylsulfoniopropionate (DMSP) degradation by marine bacteria. The C–S bond of MT can be cleaved by methanethiol oxidases (MTOs) to release a sulfur atom. However, the cleaving process remains unclear, and the species of sulfur product is uncertain. It has long been assumed that MTOs produce hydrogen sulfide (H2S) from MT. Herein, we studied the MTOs in the Rhodobacteraceae family—whose members are important DMSP degraders ubiquitous in marine environments. We identified 57 MTOs from 1,904 Rhodobacteraceae genomes. These MTOs were grouped into two major clusters. Cluster 1 members share three conserved cysteine residues, while cluster 2 members contain one conserved cysteine residue. We examined the products of three representative MTOs both in vitro and in vivo. All of them produced sulfane sulfur other than H2S from MT. Their conserved cysteines are substrate-binding sites in which the MTO–S–S–CH3 complex is formed. This finding clarified the sulfur product of MTOs and enlightened the MTO-catalyzing process. Moreover, this study connected DMSP degradation with sulfane sulfur metabolism, filling a critical gap in the DMSP degradation pathway and representing new knowledge in the marine sulfur cycle field.
IMPORTANCE
This study overthrows a long-time assumption that methanethiol oxidases (MTOs) cleave the C–S bond of methanethiol to produce both H2S and H2O2—the former is a strong reductant and the latter is a strong oxidant. From a chemistry viewpoint, this reaction is difficult to happen. Investigations on three representative MTOs indicated that sulfane sulfur (S0) was the direct product, and no H2O2 was produced. Finally, the products of MTOs were corrected to be S0 and H2O. This finding connected dimethylsulfoniopropionate (DMSP) degradation with sulfane sulfur metabolism, filling a critical gap in the DMSP degradation pathway and representing new knowledge in the marine sulfur cycle field.
KEYWORDS: DMSP, Rhodobacteraceae, methanethiol, methanethiol oxidase, H2S, sulfane sulfur
INTRODUCTION
The organosulfur compound dimethylsulfoniopropionate (DMSP) produced by marine phytoplankton, angiosperms, animals, and some heterotrophic bacteria can reach several Pg (1015 g) per year (1–3). DMSP provides important carbon and sulfur sources for marine microbial communities (4, 5). Three DMSP metabolic pathways, demethylation, oxidation, and cleavage, have been discovered in marine microorganisms (6–8). Among them, demethylation is the most important one because 50% to 90% of DMSP is processed through this pathway (9). Via the demethylation pathway, DMSP is cleaved into two major intermediates, acetaldehyde and methanethiol (MT). The former then enters the carbon cycle, whereas the latter has an uncertain fortune. It was reported that MT was assimilated or broken down to formaldehyde and H2S (10–13).
It is estimated that 1 to 1.8 Pg MT is produced from DMSP per year, and this amount does not include other MT sources, such as methylation of sulfide, degradation of sulfur-containing amino acids, and dimethyl sulfide (DMS) (14–16). Chemically, MT is a volatile compound like H2S and DMS, and only a few measurements of MT in the environment have been reported. Lomans et al. measured the MT of ditches in a minerotrophic peatland in the Netherlands and found that its concentration reached 3–76 nM in sediments and 1–8 nM in surface freshwater (17). In seawater, MT concentration was suggested to be 0.02–2 nM (18, 19). Microbial uptake and degradation are important sinks for MT. Radiotracer experiments showed that trace levels of MT (0.5 nM) were rapidly taken up and then utilized as carbon and sulfur sources by marine bacterioplankton (20). To be assimilated by bacteria, C–S bond of MT is first cleaved by methanethiol oxidase (MTO), but the cleavage process and sulfur products are uncertain (12, 21–23).
MTO was distributed in many species, including bacteria, archaea, humans, fish, birds, and plants (24–26). It was proposed that the human MTO can degrade MT into H2S, hydrogen peroxide (H2O2), and formaldehyde (HCHO) (27). Philipp et al. once used a bacterial recombinant l-methionine gamma-lyase to produce MT in situ and then used enterocyte MTO to treat the product. During this coupled enzyme assay, H2S and H2O2 were detected (28). In addition, it was observed that MTO-containing bacteria can produce H2S when they consume MT (26). It has long been assumed that in marine microorganisms, DMSP-derived MT was first degraded to H2S by MTO, which was further oxidized to sulfane sulfur (S0) by sulfide:quinone oxidoreductase (SQR) or directly used for cysteine synthesis.
Ruegeria pomeroyi DSS-3 is a model bacterium of the Rhodobacteraceae family. It is also the first sequenced heterotrophic marine bacterium and has been widely used in the study of marine sulfur metabolism. Previous studies indicate that this strain contains a well-known DMSP demethylation pathway, and the sequence analysis indicates that it contains a proposed MTO (12, 29). Therefore, it is a good candidate bacterium used in MTO study. Herein, we found out that its MTO (hereafter, we renamed it as RpMTO) catalyzed MT degradation to produce sulfane sulfur other than H2S. Two MTOs from other strains showed the same activity. Our findings clarified the sulfur product of the MTO-catalyzed MT degradation reaction and filled a critical gap in the DMSP degradation pathway.
RESULTS
RpMTO degraded MT but produced no H2O2
Marine bacterium R. pomeroyi DSS-3 degrades DMSP to produce MT via the demethylation pathway. It also contains an RpMTO (WP_011242048.1) encoded by SPOA0269, suggesting that it can also degrade MT. We cloned the RpMTO-encoding gene and expressed it in Escherichia coli BL21 (DE3). The expressed RpMTO (fused with an N-terminal His-Tag) was purified using a nickel column. During cell disruption and protein purification processes, no dithiothreitol (DTT) or other reductants were added. The SDS-PAGE analysis indicated that its molecular weight was around 55 kDa (Fig. 1A), near the calculated molecular weight (50.4 kDa).
Fig 1.
Characterization of RpMTO and analysis of its products. (A) SDS-PAGE analysis of the purified RpMTO. The left lane is a weight marker, and the right lane is RpMTO. (B) The standard calculation curve of the Peroxide Assay Kit method made in this study. (C) Using Peroxide Assay Kit to analyze the produced H2O2 from enzymatic reaction. (D) The standard calculation curve of the horseradish peroxidase (HRP)-catalyzed 10-acetyl-3,7-dihydroxyphenox-azine (ADHP) method made in this study. (E) Using HRP-catalyzed ADHP to analyze the produced H2O2 from enzymatic reaction. (F) Products from the chemical reaction of H2S with H2O2. High-performance liquid chromatograph (HPLC) spectra of them are provided in Fig. S1. HSSH, hydrogen persulfide.
Freshly purified enzyme was subjected to activity analysis. According to the assumed activity, RpMTO can degrade MT in the presence of oxygen to produce HCHO, H2S, and H2O2 (reaction 1).
| (1) |
To test its activity, we mixed purified RpMTO with MT. The gas chromatography-mass spectrometry (GC–MS) analysis indicated that 77 µM MT was oxidized by RpMTO. We then tried to quantify the produced H2O2. A commercial H2O2 assay kit was used. According to our test, the detection limit of this kit was about 10 µM (Fig. 1B). However, in the above-mentioned reacting conditions, no H2O2 product was detected from the RpMTO-catalyzing reaction by this kit. We then increased the MT concentration to 1–3 mM. Still, only around 10 µM H2O2 or less was detected (Fig. 1C). Considering that both the proteins RpMTO and MT have weak absorbance at 560 nm, and 10 µM was on the edge of the kit’s detection limit, the detected H2O2 concentration cannot be trusted.
We then used the H2O2 fluorescence probe 10-acetyl-3,7-dihydroxyphenox-azine (ADHP) for detection. According to our test, this probe can detect as low as 0.5 µM H2O2 (Fig. 1D). To avoid potential disturbance, RpMTO was precipitated down by acetonitrile and removed by centrifugation after the reaction. Only about 0.005 µM H2O2 was detected even when MT was increased to 10 mM (Fig. 1E). Therefore, the detected H2O2 concentration with the ADHP probe cannot be trusted either.
It is possible that the produced H2O2 quickly reacted with H2S and was completely consumed in reaction 2 (unbalanced).
| (2) |
To test this possibility, we mixed equal amounts of H2O2 and H2S. The produced sulfur-containing compounds were derivatized with monobromobimane (mBBr) and subjected to HPLC analysis. Sulfite, thiosulfate, and hydrogen persulfide (HSSH) were detected (Fig. 1F; Fig. S1). However, when using the same method to analyze the products of the RpMTO-catalyzing reaction, no sulfite or thiosulfate was detected. These results suggested that reaction 2 was not involved in the process of RpMTO-catalyzed MT degradation. Combining the above results, we concluded that no H2O2 was produced by RpMTO; that is, RpMTO did not catalyze reaction 1.
RpMTO produced sulfane sulfur rather than H2S from MT
To examine the sulfur-containing products generated from the RpMTO-catalyzing reaction, purified RpMTO was mixed with MT. The products were derivatized with mBBr and analyzed by liquid chromatography-electrospray ionization-mass spectrometry (LC–ESI-MS). Again, no sulfite or thiosulfate derivative was detected. H2S derivatives mB–SH and mB–S–mB were present. The signal intensity of the former was 4.0 × 106 and the latter was 2.5 × 105 (Fig. 2A; Fig. S2). Surprisingly, the derivative of HSSH (mB–SSH) was also present, and its signal intensity was 9.6 × 106 (Fig. S3), which was much higher than that of H2S derivatives. The remaining MT can be derivatized by mBBr to form CH3–S–mB. This derivative compound also was present with a signal intensity of 3 × 104 (Fig. S4).
Fig 2.

LC–ESI-MS analysis of the sulfur products produced by RpMTO. (A) MS signal intensities of sulfur products from RpMTO-catalyzed MT degradation. mB–SH and mB–S–mB are H2S derivatives (by mBBr); mB–SSH is an HSSH derivative, and CH3–S–mB is an MT derivative. (B) The MS signal intensities of sulfur products from the control experiment (no RpMTO). MS spectra of them are provided in Fig. S4.
As the control, we also diluted MT in reaction buffer without RpMTO and then derivatized with mBBr. The LC–ESI-MS analysis indicated that except for CH3–S–mB, mB–SH also was present with a signal intensity of 3 × 106 (Fig. 2B). No mB–S–mB was present. These results were unexpected because we did not know why and how mBBr reacted with methanethiol to generate mB–SH but not mB–S–mB. Nonetheless, the critical finding was that no HSSH derivative mB–SSH was present, indicating that sulfane sulfur species HSSH was only produced from the RpMTO-catalyzing reaction; however, H2S was not produced.
To examine whether the amount of the produced sulfane sulfur was equal to another product HCHO, we quantified both products in the enzymatic reaction system. The amount of sulfane sulfur atom (quantified as the total sulfane sulfur by the cyanide method) was 20.0 ± 4.3 µM, while that of HCHO was 24.9 ± 1.9 µM. The ratio was 0.8:1, a little less than 1:1, probably because a portion of the produced sulfane sulfur became H2S.
In 1987, Suylen et al. once detected sulfane sulfur from Hyphomicrobium sp. strain EG MTO catalyzed MT oxidation (22). They proposed that the product was from reaction 3.
| (3) |
However, when we incubated the H2S solution at the aerobic condition for 30 min, no sulfane sulfur production was detected. In addition, reaction 3 is against our observations of H2S-related experiments, from which we found that H2S was not readily oxidized by oxygen without the help of related enzymes/oxidants. Therefore, we concluded that the sulfane sulfur detected from the RpMTO-catalyzing reaction was not from reaction 3.
RpMTO produced sulfane sulfur in vivo
We used three R. pomeroyi DSS-3 mutants to further verify the sulfur product of RpMTO in vivo, the first one is ∆pdo, in which the persulfide dioxygenase-encoding gene pdo was deleted. Therefore, this strain loses sulfane sulfur oxidation activity and can accumulate sulfane sulfur inside cells. The second one is ∆sqr∆fccAB, in which the H2S oxidation enzyme-encoding genes sqr and fccAB were deleted. Therefore, this strain loses H2S oxidation activity and can release H2S into culture once it is produced intracellularly (H2S easily passes through the cell membrane). The third one is ∆mtoX, in which the RpMTO-encoding gene was deleted. This strain was used as a negative control.
We mixed cells of R. pomeroyi DSS-3 wild type (wt) and three mutants with MT individually. After 2 h incubation, H2S in the cell-MT culture and sulfane sulfur in cells were quantified (H2S is cell membrane permeable but sulfane sulfur is not). The latter was quantified as the total sulfane sulfur using an HPLC-based method (30). Theoretically, if H2S is the direct product of RpMTO, it will accumulate in ∆sqr∆fccAB culture but not in ∆pdo culture. The results showed that, on the contrary, ∆sqr∆fccAB culture did not accumulate more H2S than the other three cultures (Fig. 3A). ∆pdo culture was the one that accumulated the highest concentration of H2S. Previous studies have indicated that a high concentration of intracellular sulfane sulfur is toxic to cells. To decrease the sulfane sulfur level, cells either oxidize sulfane sulfur to less toxic sulfite or reduce it to releasable H2S via glutathione (GSH) or enzyme-mediated reactions. For strains that have no persulfide dioxygenase (PDO) (such as E. coli and yeast), they cannot conduct the oxidation reaction, and hence, reduction is the only choice (30, 31). This should be the reason why Δpdo culture accumulated more H2S than the others. Its H2S was from the reduction of the RpMTO-produced sulfane sulfur.
Fig 3.
MT degradation and product analysis of RpMTO-containing strains. (A) Hydrogen sulfide production from R. pomeroyi DSS-3 wt and mutants. (B) Sulfane sulfur production from R. pomeroyi DSS-3 wt and mutants. (C) MT consumed by R. pomeroyi DSS-3 wt and mutants. (D) Sulfane sulfur production from E. coli BL21(DE3) containing the plasmid pET28a-RpMTO. t-tests were performed to calculate the P-values, and asterisks indicate statistically significant differences (∗P < 0.05, ∗∗P < 0.01, ∗∗∗P < 0.001). ns, no significant difference.
On the other hand, if sulfane sulfur is the direct product of RpMTO, sulfane sulfur will accumulate in ∆pdo cells but not in ∆sqr∆fccAB cells because PDO in the latter is still active and can oxidize the produced sulfane sulfur to sulfite. The results, indeed, showed that ∆pdo cells accumulated significantly higher amounts of intracellular sulfane sulfur than ∆sqr∆fccAB cells did (Fig. 3B).
Theoretically, if the PDO-mediated sulfane sulfur oxidation pathway is impeded, the RpMTO-catalyzed MT degradation should be affected due to the accumulation of sulfane sulfur, which is toxic to cells at high concentrations (30, 31). To check this, we used GC–MS to analyze the MT degradation capabilities of wt and three mutants. The wt metabolized 0.53 ± 0.16 mM MT, and ∆sqr∆fccAB metabolized 0.39 ± 0.15 mM MT. In comparison, ∆pdo metabolized 0.18 ± 0.05 mM MT (Fig. 3C). These results indicated that blocking the sulfane sulfur oxidation pathway in R. pomeroyi DSS-3, indeed, severely impeded its MT degradation capability, whereas blocking H2S oxidation pathway just had mild influence. In addition, ∆mtoX lost most of the MT degradation activity (metabolized only 0.03 ± 0.02 mM MT), and it produced almost no H2S and the lowest amount of sulfane sulfur (Fig. 3A through C). These results indicated that RpMTO was the critical enzyme for MT degradation in R. pomeroyi DSS-3.
E. coli BL21(DE3) contains no H2S or sulfane sulfur oxidation enzymes (no SQR, flavocytochrone c sulfide dehydrogenase (FCC), or PDO), which makes it a clean background for testing RpMTO activity. We constructed a pET28a-RpMTO plasmid and transformed it into E. coli BL21(DE3). The strain was induced by isopropyl β-D-1-thiogalactopyranoside (IPTG), and then 10 mL cell suspension (OD600 = 3.0) was collected. We mixed MT with this cell suspension. After 1 h incubation, both H2S and sulfane sulfur were quantified. Cell suspension without MT addition was used as a control. H2S was not produced by the experimental group (cells mixed with MT) or control, and the experimental group produced more intracellular sulfane sulfur than the control did (Fig. 3D). The above results confirmed that sulfane sulfur, other than H2S, was the product of RpMTO in vivo.
The cysteine residue Cys28 was required for RpMTO activity
The other enzymes that catalyze C–S bond breakage, such as 3-mercaptopyruvate sulfurtransferase (3-MST) and cystathionine β-synthase (CBS), require cysteine residues for their activities (32, 33). To check whether RpMTO is the same case, we mutated the only cysteine of RpMTO (Cys28) to serine. The mutant RpMTOC28S was expressed in E. coli and purified using a nickel column. We used the sulfane sulfur-producing ability to judge its activity. After mixing purified RpMTOC28S with MT, sulfane sulfur production was barely detected, suggesting that Cys28 was required for MT degradation activity (Fig. 4A).
Fig 4.
Characterization of RpMTO mutant, its peptide, and modeled structure. (A) RpMTOC28S mutant lost sulfane sulfur-producing activity. (B) LC–MS/MS analysis of MT-treated and untreated RpMTO. MS2 spectra of the peptides are provided in Fig. S8. (C) Modeled structure of RpMTO using AlphaFold 2. The conserved cysteine residue (Cys28) is shown as sticks, ∗, P < 0.05.
To check how RpMTO reacts with MT, purified RpMTO was incubated with MT. The MT treated-RpMTO was labeled with iodoacetamide (IAM) and then subjected to trypsin digestion, followed by LC–MS/MS analysis. RpMTO without MT treatment was used as a control. For the MT-treated RpMTO, three Cys28-containing peptides were identified (Fig. 4B). In peptide 1, Cys28 residue was directly blocked by IAM to form Cys28–S–AM (+57.02 Da) (Fig. S5). In peptide 2, a mass increase of 88.99 Da on Cys28 residue was identified (Fig. S6), suggesting that Cys28–S–S–H was blocked by IAM to form Cys28–S–S–AM. In peptide 3, a mass increase of 45.99 Da on Cys28 residue was identified, corresponding to Cys28–S–S–CH3 modification (Fig. S7). For the MT-untreated RpMTO control, only a peptide with Cys28–S–AM modification was identified (+57.02 Da, peptide 4), corresponding to the direct blockage of Cys28 residue by IAM (Fig. S8). These results suggested that RpMTO used its Cys28 residue to bind MT to form a Cys28–S–S–CH3 complex.
The 3D structure of RpMTO was modeled using AlphaFold 2. The modeled structure shows that Cys28 is located in an incompact, cave-like position formed by random coils (Fig. 4C). This position is near the RpMTO surface, which makes Cys28 accessible to MT. Therefore, MT should first enter this position and then react with Cys28.
Two types of MTO are present in Rhodobacterales
Using R. pomeroyi DSS-3 RpMTO as the query to search homologs from Rhodobacterales genomes, we identified 57 MTOs. Most of them are predicted selenium-binding proteins. The phylogenetic tree shows that they can be grouped into two major clusters (Fig. 5). Cluster 1 contains 49 members, which are further grouped into two branches. Cluster 2 contains eight members including R. pomeroyi DSS-3 RpMTO.
Fig 5.
Phylogenetic analysis of 57 MTO candidates obtained from Rhodobacteraceae family. Three representative MTOs (RpMTO, RdMTO, and RlMTO) are highlighted with red dots.
Similar to R. pomeroyi DSS-3 RpMTO, the other seven members of cluster 2 also contain only one cysteine residue. We aligned their protein sequences and found that this cysteine residue conserves in all of them (Fig. 6A; Fig. S9). In addition, the neighboring residues also conserve as a “TCQSPYM” sequence. These analyses suggest that all cluster 2 MTOs catalyze MT degradation via the same mechanism.
Fig 6.
Amino acid sequence alignment of cluster 1 (A) and 2 (B) members. The conserved cysteine residues are marked with an asterisk. For cluster 2, not all members are shown here. Full sequence alignments of full members of both clusters are provided in Fig. S9 and S10.
Different from cluster 2 MTOs, cluster 1 MTOs contain multiple cysteine residues. Protein sequence alignment indicates that there are three conserved cysteine residues in most of them, located in three conserved sequences “GWNACS,” “HTV(I)HC,” and “GGDCS(T),” respectively (Fig. 6B; Fig. S10).
Cluster 1 MTOs also produced sulfane sulfur from MT
Roseobacter denitrificans OCh114 is one of the most studied bacteria of the Roseobacter lineage (34). Ruegeria lacuscaerulensis ITI_1157 contains genes responsible for DMSP decomposition to produce MT (35, 36). They both have hypothetical MTOs (WP_011568565.1 and EEX10901.1, respectively). We chose their MTOs as representatives of cluster 1. MTOs of R. denitrificans OCh114 (renamed as RdMTO) and R. lacuscaerulensis ITI_1157 (renamed as RlMTO) were expressed in E. coli BL21(DE3) and purified with nickel columns. After mixing purified MTOs with MT, GC–MS analysis was performed to analyze MT degradation. RdMTO and RlMTO consumed 44 and 111 µM MT, respectively. The LC–ESI-MS analysis indicated that the signal intensity of H2S derivatives (mB–SH and mB–S–mB) from RdMTO were 1.9 × 106 and 2.8 × 105, respectively, whereas the signal intensity of the HSSH derivative (mB–SSH) was 4.5 × 106 (Fig. 7A). The signal intensity of the two H2S derivatives from RlMTO were 1.6 × 106 and 0.8 × 105, respectively, whereas the signal intensity of HSSH derivative was 6.0 × 106. For both enzymes, they produced more HSSH than H2S (Fig. 7B). In addition, as RpMTO, they did not produce H2O2.
Fig 7.
Analysis of RdMTO and RlMTO activities. (A) MS signal intensities of sulfur products from RdMTO-catalyzed MT degradation. (B) MS signal intensities of sulfur products from RlMTO-catalyzed MT degradation. (C) Sulfane sulfur production from E. coli BL21 (DE3) containing pET28a-RdMTO or pET28a-RlMTO. (D) Compared with RdMTO (wt), its three cysteine-to-serine mutants showed lower sulfane sulfur-producing activity. (E) Compared with RlMTO wt, the three cysteine-to-serine mutants showed lower sulfane sulfur-producing activity. (F) LC–MS/MS analysis of MT-treated and MT-untreated RdMTO. The RdMTO 3D structure modeled by AlphaFold 2. MS2 data of the peptides are provided in Fig. S11 to S13. (G) LC–MS/MS analysis of MT-treated and MT-untreated RlMTO. The RlMTO 3D structure modeled by AlphaFold 2. MS2 data of the peptides are provided in Fig. S14 and S15. (I) Non-reduced SDS-PAGE analysis of the MT-treated (MT+) and MT-untreated (MT−) RdMTO and RlMTO. For panels C and D, t-tests were performed to calculate the P-values, and asterisks indicate statistically significant differences (∗P < 0.05, ∗∗P < 0.01, ∗∗∗∗P < 0.0001).
To test their activities in vivo, we used E. coli BL21(DE3) harboring pET28a-RdMTO or pET28a-RlMTO plasmids. The strains were induced by IPTG. Cell suspensions (OD600 = 3.0) were collected and mixed with MT. Cell suspensions without MT addition were used as controls. Again, no H2S production was detected, and both RdMTO and RlMTO expressing E. coli cells produced more intracellular sulfane sulfur than controls did (Fig. 7C), indicating that RdMTO and RlMTO also catalyzed MT degradation to produce sulfane sulfur in vivo.
Conserved cysteine residues were required for MT degradation for cluster 1
The three conserved cysteine residues in RdMTO and RlMTO were mutated to serine residues individually. The six mutants, RdMTOC82S, RdMTOC143S, RdMTOC448S, RlMTOC76S, RlMTOC140S, and RlMTOC456S, were expressed in E. coli and purified using nickel columns. As the RpMTOC28S mutant, RdMTO and RlMTO mutants also lost most of the sulfane sulfur-producing activity (Fig. 7D through E), indicating that all their conserved cysteine residues were required for the MT degradation activity.
Purified RdMTO and RlMTO were incubated with MT. The MT-treated enzymes were labeled with IAM and subjected to trypsin digestion, followed by LC–MS/MS analysis. MT-untreated enzymes were used as controls. For MT-treated RdMTO and RlMTO, a common feature was that Cys–S–S–CH3 modification was observed in their third conserved cysteine residues (RdMTOC448 and RlMTO C456) (Fig. 7G and H; Fig. S11 to S15). No such modification was observed in MT-untreated enzymes. These results suggested that these enzymes used the third conserved cysteine residues to react with MT.
3D structures of RdMTO and RlMTO were also modeled using AlphaFold 2. Similar to the case of RpMTO, active cysteine residues of both RdMTO (Cys448) and RlMTO (Cys456) are located in incompact, cave-like positions. A difference is that their caves are looser and larger than that of RpMTO. The other two cysteines are located in very compact positions surrounded by β-sheets (Fig. 7G and H).
Non-reduced SDS-PAGE analysis indicated that freshly purified RdMTO and RlMTO were both monomers. After mixing with MT, a portion of them became dimers or tetramers (Fig. 7I). The other two cysteine residues not involved in MT binding might be involved in this process. To test this hypothesis, we performed a non-reduced SDS-PAGE analysis with RdMTO and its Cys-to-Ser mutants. RdMTO mutants containing C143S mutation all lost the dimer formation capability (Fig. S16), implying that Cys143 plays a critical role in the dimer formation process.
DISCUSSION
The Rhodobacteraceae family is important DMSP degrader in marine environments. To achieve the final degradation of DMSP, its C–S bond needs to be cleaved to release the sulfur atom. This process is catalyzed by MTOs. The mechanism of MTO functions and the produced sulfur species remain uncertain. In this work, we studied the MTOs of the Rhodobacteraceae family. We identified 57 MTOs from 1,904 Rhodobacteraceae genomes. These MTOs were grouped into two major clusters. We examined the products of three representative MTOs (RpMTO, RdMTO, and RlMTO) both in vitro and in vivo. All of them produced sulfane sulfur other than H2S from MT. This finding is different from previous reports (21, 22, 37). We also found that MTO-conserved cysteines are substrate-binding sites in which the MTO–S–S–CH3 complex is formed. Our study clarified the product of MTO and enlightened the MTO-catalyzing process, filling a critical gap in the DMSP degradation pathway.
H2S has been recognized as an enzyme-mediated, intracellularly produced, sulfur-metabolizing intermediate for a long time. As for sulfane sulfur, realizing that it is commonly present inside cells and much more abundant than H2S just happened in the recent decade (38, 39). Intracellular sulfane sulfur exists in different forms, including Cys–SnH, GSnH, and HSnH (n ≥ 2). They are very reactive and easily reduced to H2S by reducing powers like GSH. Therefore, sulfane sulfur and H2S often coexist. The former was ignored for a long time because its detection was difficult, but new methods were quickly developed in recent decades (40, 41). Accompanied by the methodology development, some enzymes, such as 3-MST and CBS that previously were thought to be H2S-producing enzymes, are now considered sulfane sulfur-producing enzymes (42, 43). Actually, the finding that MTOs produce sulfane sulfur other than H2S is not surprising because, in previous reports of MTO-related studies (25, 27), no sulfane sulfur-detecting experiment was conducted. In 2018, Eyice et al. studied the catalyzing kinetics of RpMTO and analyzed its MT consumption and formaldehyde production, but they did not analyze its sulfur products either (12). In addition, during the enzyme purification process, reductants like DTT were often added, which can reduce sulfane sulfur to H2S, just like GSH does inside cells. This easily led to the wrong conclusion that H2S was the direct product of MTOs. In our experiments, we avoided adding DTT during MTO purification and only used freshly purified proteins for enzymatic analysis. This should be the key reason why we detected sulfane sulfur production.
Protein LC–MS/MS analysis indicated that the conserved cysteine residues in “GGDCS(T)” of cluster 1 MTO and in “TCQSPYM” of cluster 2 MTO are the catalyzing sites. We proposed that MT first reacts with conserved cysteine to form Cys–S–S–CH3 additive, and then O2 attacks this additive to break its C–S bond to produce HCHO and Cys–S–S–H. Since RSSH disulfide is inherently unstable (44, 45), Cys–S–S–H easily releases a sulfane sulfur atom and turns back to Cys–SH (Fig. 8A). Other amino acids spatially adjacent to the conserved cysteine residue may help in the O2 attack and S0 detachment processes. Finally, since no H2O2 production was detected, we proposed that the MTO-catalyzing reaction can be rewritten to reaction 4.
Fig 8.
A proposed mechanism to explain how RpMTO catalyzes MT degradation to produce sulfane sulfur (A) and the connection of DMSP degradation with sulfur metabolism (B). DMSP, dimethylsulfoniopropionate; MMPA, methylmercaptopropionate.
| (4) |
According to the modeled structures of three MTOs, their catalyzing cysteine residues are all located in cave-like positions formed by random coils. Differently, the other two cysteines of RdMTO and RlMTO are located in a compact position surrounded by β-sheets. Therefore, MT may be accessible only to catalyzing cysteine. In consistent with our results, LC–MS/MS analysis indicated that Cys–S–S–CH3 additive only formed in catalyzing cysteine. However, mutating the two non-catalyzing cysteines also leads to impaired activity, demonstrating that they are not dispensable. Non-reduced SDS-PAGE analysis indicates that they are needed for dimer or tetramer formation. However, the current study of MTO is short, and whether these two cysteines are located in the oligomer formation domain is still unknown. In addition, RpMTO has a high sequence similarity (56.67%) with MTO of Hyphomicrobium sp. VS. The latter contains copper ions according to Eyice et al. (12). RpMTO also has conserved Trp223 and Trp386, which are supposed to be involved in the formation of a tryptophan tryptophylquinone (TTQ) cofactor. It also has His88/89, His141, and His424, which are putative copper ligands close to the TTQ (Fig. S17). Therefore, its catalyzing mechanism should be the same as the MTO of Hyphomicrobium sp. VS.
In conclusion, MT is an important intermediate connecting the metabolisms of organic sulfur and inorganic sulfur. In this work, we found that MTOs degraded MT, and the direct product was sulfane sulfur rather than H2S. This finding patches an important gap in the whole DMSP degradation pathway and correctly connects DMSP degradation with sulfane sulfur metabolism (Fig. 8B). Previously, it was thought that the sulfur atom in DMSP became H2S and then entered H2S metabolic pathway (mostly via SQR oxidation). Now, we change the route to the sulfane sulfur metabolic pathway (no SQR involved). The correction makes DMSP not only a sulfur source but also a sulfane sulfur donor, suggesting that DMSP may be involved in many regulation functions as other sulfane sulfur donors commonly do (46, 47).
MATERIALS AND METHODS
Strains and cultivation conditions
R. pomeroyi DSS-3, R. denitrificans, and R. lacuscaerulensis are gifts from Prof. Yuzhong Zhang of the Ocean University of China. R. pomeroyi DSS-3 derivatives ∆pdo and ∆sqr∆fccAB were constructed previously in our lab (48). R. pomeroyi DSS-3 ∆mtoX was constructed using previously reported methods (49, 50). Details of the construction method are provided in the supplemental material. E. coli strains used for plasmid construction and protein expression, plasmids constructed in this study are all listed in Table S1. R. pomeroyi DSS-3 strain was cultured in the 1/2 YTSS medium, which contains 4 g/L yeast extract, 2.5 g/L tryptone, and 20 g/L sea salts. For cultivation, R. pomeroyi DSS-3 strains were cultivated at 30°C with shaking (220 rpm). E. coli strains were cultured in lysogeny broth (LB) medium at 37°C.
Sodium hydrosulfide (NaHS) was purchased from Sigma-Aldrich (Saint Louis, MO). Hydrogen Peroxide Assay Kit was purchased from Beyotime Biotechnology (Shanghai, China). MT was purchased from Macklin Biochemical Co., Ltd (Shanghai, China), and ADHP and horseradish peroxidase (HRP) enzymes were purchased from Aladdin Biotech (Shanghai, China).
Protein expression and purification
RpMTO-encoding gene was amplified from the genomic DNA of R. pomeroyi DSS-3. RdMTO- and RlMTO-encoding genes were amplified from R. denitrificans and R. lacuscaerulensis genomic DNA, respectively. Their cysteine-to-serine mutants were constructed using the QuickChange method (51). Primers used for gene expression and mutation are listed in Table S2. For MTO expression and purification in E. coli, a His-tag was fused to their N-terminus, and pET28a plasmid was used. More details of the expression and purification experiments are provided in the supplemental material.
Enzymatic activity assay
MT was dissolved in propanediol (1.8 M). The enzymatic reaction was performed in 0.3 mL reaction buffer (50 mM Tris-HCl, pH 8.4) in a 1.5 mL scale tube. In the reaction buffer, purified MTO (0.3 mg/mL) was mixed with 0.6–3 mM MT. The reaction was performed at 30°C for 30 min. As a control, boiled enzyme (inactive) was also mixed with MT in the same reaction system. After the reaction, the produced H2O2 was quantified using a Hydrogen Peroxide Assay Kit or HRP-catalyzed ADHP method. The remaining MT was quantified by GC–MS. The amount of enzyme-degraded MT was calculated by subtracting MT in control (deemed as vaporized amount) from MT in the reaction system. For sulfur species determination, the products in the reaction system were derivatized with mBBr and then subjected to LC–ESI-MS analysis. The total concentration of the produced sulfane sulfur was quantified with the cyanide method (52). The produced formaldehyde was quantified using a previously reported method.
Details of H2O2, MT, sulfur species, and formaldehyde quantification are provided in the supplemental material.
Chemical reaction and product analysis
Reaction of H2S with H2O2 was performed as reported previously (53). Briefly, 50 µM H2S was added to 50 µM H2O2 in deoxygenated Tris-HCl buffer (50 mM, pH 8.4). The reaction was conducted at room temperature for 30 min. Products were labeled with mBBr and quantified by HPLC following the protocol (54). The reaction of H2S with oxygen and product analysis was performed following the same protocol as the H2S reaction with H2O2, except that no H2O2 was added, and the reaction solution was not deoxygenated. Oxygen dissolved in the reaction solution was deemed as the reactant.
Analysis of MTO products in vivo
The R. pomeroyi DSS-3 strains were cultured in 1/2 YTSS medium overnight. The overnight culture (1 mL) was transferred into 100 mL of fresh medium and cultured to OD600 = 2.0. Cells were collected by centrifugation (4,000 × g, 5 min) and re-suspended in Tris-HCl buffer (pH 8.4, 50 mM, 20 mM MgCl2, 20 g/L NaCl) to make OD600 = 5.0. Three E. coli BL21(DE3) strains harboring pET28a-RpMTO, pET28a-RdMTO, or pET28a-RlMTO plasmid were incubated in LB medium containing kanamycin (50 µg/mL). When OD600 reached 0.6, 0.4–0.6 mM IPTG was added, and the temperature was decreased to 25°C. After 16 h cultivation, cells were harvested by centrifugation and then re-suspended in Tris-HCl buffer to make OD600 = 3.0.
MT (1 mM) was added to 10 mL cell suspension in a 50 mL scale tube. The tube was then incubated at 30°C for 2 h with shaking (200 rpm). To quantify the produced H2S, 50 µL supernatant was taken after centrifugation. The supernatant was derivatized with mBBr and then quantified by HPLC following a previously reported protocol (54). Sulfane sulfur quantification was performed using an HPLC-based method reported previously (39). Briefly, R. pomeroyi DSS-3 and E. coli cells (treated with 1 mM MT) were collected and re-suspended in 100 µL reaction buffer (50 mM Tris-HCl, pH 9.5, 1% Triton X-100, 50 µM DTPA, and 0.5 mM sulfite) and incubated at 95°C for 10 min to convert intracellular sulfane sulfur atom into thiosulfate. The produced thiosulfate was labeled with mBBr and quantified by HPLC. The obtained sulfane sulfur amount was deemed as total sulfane sulfur.
LC–MS/MS analysis of MTO
Purified MTO (0.3 mg/mL) was mixed with 0.6 mM MT in Tris-HCl buffer (pH 8.4, 50 mM). After incubating the mixture at 30°C for 30 min, the denaturing buffer (0.5 M Tris-HCl, 2.75 mM EDTA, 6 M guanadine-HCl, and pH 8.1) with excess iodoacetamide (0.5 M) was added to denaturalize MTO and block free thiols. LC–MS/MS analysis was performed following a previously reported protocol (55, 56). More details are provided in the supplemental material.
SDS-PAGE and non-reduced SDS-PAGE analysis
For SDS-PAGE analysis, the purified protein was added to 5× loading buffer (CWBIO, Beijing, China) in a ratio of 5:1. After incubating the mixture at 95°C for 10 min, the sample was subjected to gel electrophoresis. For non-reduced SDS-PAGE, the loading buffer did not contain DTT. After electrophoresis, the gel was stained for 5–10 min and then placed in FluorChem Q (Thermo Fisher, Waltham, MA, USA) for imaging. To investigate how MT affects MTO status, purified MTO was divided into two portions, and the control portion was not treated with MT. The reaction portion was reacted with 1 mM MT at 30°C for 30 min. The denaturing buffer (0.5 M Tris-HCl, 2.75 mM EDTA, 6 M guanadine-HCl, and pH 8.1) with excess IAM (0.5 M) was added to denaturalize protein and block free thiols. Finally, a non-reduced SDS-PAGE analysis was performed.
MTO structure modeling
The AlphaFold 2 algorithm (57) was used to model the tertiary structure of three MTOs. This method used the custom multiple sequence alignment option and was accessed via the Colab server on GitHub (https://github.com/sokrypton/ColabFold). The structural models of MTOs were analyzed and visualized with PyMOL (Version 1.5.0.3).
Bioinformatic analysis
Rhodobacterales genomes were downloaded from the NCBI database (1904, update to 6 June 2022), and redundancy was removed using the CD-HIT tool. MTO candidate genes (a total of 57) in Rhodobacterales genomes were obtained by searching the database with the standalone BLASTP algorithm using conventional criteria (E value of ≤1e−5, coverage of ≥45%, and identity of ≥25%). A phylogenetic tree was constructed by a neighbor-joining method using MEGA 7.0 with a partial deletion, p-distance distribution, and bootstrap at 1,000 repeats. Multiple sequence alignment was performed using Clustal Omega.
Statistical information
Data of Fig. 1C, Fig. 1E, Fig. 1F, Fig. 2C, Fig. 3A through D, Fig. 4A, and Fig. 7C through E were obtained from three independent replicates and shown as average ± SD.
ACKNOWLEDGMENTS
This work was supported by the National Key R&D Program of China (2022YFC3401301) and the National Natural Science Foundation of China (91951202).
Contributor Information
Huaiwei Liu, Email: liuhuaiwei@sdu.edu.cn.
Oladele A. Ogunseitan, University of California, Irvine, Irvine, California, USA
SUPPLEMENTAL MATERIAL
The following material is available online at https://doi.org/10.1128/mbio.02907-23.
Methods, Tables S1 and S2, and Figures S1-S17.
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. Ksionzek KB, Lechtenfeld OJ, McCallister SL, Schmitt-Kopplin P, Geuer JK, Geibert W, Koch BP. 2016. Dissolved organic sulfur in the ocean: biogeochemistry of a petagram inventory. Science 354:456–459. doi: 10.1126/science.aaf7796 [DOI] [PubMed] [Google Scholar]
- 2. Curson ARJ, Williams BT, Pinchbeck BJ, Sims LP, Martínez AB, Rivera PPL, Kumaresan D, Mercadé E, Spurgin LG, Carrión O, Moxon S, Cattolico RA, Kuzhiumparambil U, Guagliardo P, Clode PL, Raina J-B, Todd JD. 2018. DSYB catalyses the key step of dimethylsulfoniopropionate biosynthesis in many phytoplankton. Nat Microbiol 3:430–439. doi: 10.1038/s41564-018-0119-5 [DOI] [PubMed] [Google Scholar]
- 3. Zhang XH, Liu J, Liu JL, Yang GP, Xue CX, Curson ARJ, Todd JD. 2019. Biogenic production of DMSP and its degradation to DMS-their roles in the global sulfur cycle. Sci China Life Sci 62:1296–1319. doi: 10.1007/s11427-018-9524-y [DOI] [PubMed] [Google Scholar]
- 4. Kiene RP, Linn LJ, Bruton JA. 2000. New and important roles for DMSP in marine microbial communities. Journal of Sea Research 43:209–224. doi: 10.1016/S1385-1101(00)00023-X [DOI] [Google Scholar]
- 5. Yoch DC. 2002. Dimethylsulfoniopropionate: its sources, role in the marine food web, and biological degradation to dimethylsulfide. Appl Environ Microbiol 68:5804–5815. doi: 10.1128/AEM.68.12.5804-5815.2002 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6. Li CY, Wang XJ, Chen XL, Sheng Q, Zhang S, Wang P, Quareshy M, Rihtman B, Shao X, Gao C, Li FC, Li SY, Zhang WP, Zhang XH, Yang GP, Todd JD, Chen Y, Zhang YZ. 2021. A novel ATP dependent dimethylsulfoniopropionate lyase in bacteria that releases dimethyl sulfide and acryloyl-CoA. Elife 10:e64045. doi: 10.7554/eLife.64045 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7. Teng Z-J, Qin Q-L, Zhang W, Li J, Fu H-H, Wang P, Lan M, Luo G, He J, McMinn A, Wang M, Chen X-L, Zhang Y-Z, Chen Y, Li C-Y. 2021. Biogeographic traits of dimethyl sulfide and dimethylsulfoniopropionate cycling in polar oceans. Microbiome 9:207. doi: 10.1186/s40168-021-01153-3 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8. Thume K, Gebser B, Chen L, Meyer N, Kieber DJ, Pohnert G. 2018. The metabolite dimethylsulfoxonium propionate extends the marine organosulfur cycle. Nature 563:412–415. doi: 10.1038/s41586-018-0675-0 [DOI] [PubMed] [Google Scholar]
- 9. Kiene RP. 1996. Production of methanethiol from dimethylsulfoniopropionate in marine surface waters. Marine Chemistry 54:69–83. doi: 10.1016/0304-4203(96)00006-0 [DOI] [Google Scholar]
- 10. Howard EC, Henriksen JR, Buchan A, Reisch CR, Bürgmann H, Welsh R, Ye W, González JM, Mace K, Joye SB, Kiene RP, Whitman WB, Moran MA. 2006. Bacterial taxa that limit sulfur flux from the ocean. Science 314:649–652. doi: 10.1126/science.1130657 [DOI] [PubMed] [Google Scholar]
- 11. Reisch CR, Stoudemayer MJ, Varaljay VA, Amster IJ, Moran MA, Whitman WB. 2011. Novel pathway for assimilation of dimethylsulphoniopropionate widespread in marine bacteria. Nature 473:208–211. doi: 10.1038/nature10078 [DOI] [PubMed] [Google Scholar]
- 12. Eyice Ö, Myronova N, Pol A, Carrión O, Todd JD, Smith TJ, Gurman SJ, Cuthbertson A, Mazard S, Mennink-Kersten MA, Bugg TD, Andersson KK, Johnston AW, Op den Camp HJ, Schäfer H. 2018. Bacterial SBP56 identified as a Cu-dependent methanethiol oxidase widely distributed in the biosphere. ISME J 12:145–160. doi: 10.1038/ismej.2017.148 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13. Shaw DK, Sekar J, Ramalingam PV. 2022. Recent insights into Oceanic dimethylsulfoniopropionate biosynthesis and catabolism. Environ Microbiol 24:2669–2700. doi: 10.1111/1462-2920.16045 [DOI] [PubMed] [Google Scholar]
- 14. Bentley R, Chasteen TG. 2004. Environmental VOSCs - formation and degradation of dimethyl sulfide, methanethiol and related materials. Chemosphere 55:291–317. doi: 10.1016/j.chemosphere.2003.12.017 [DOI] [PubMed] [Google Scholar]
- 15. Carrión O, Pratscher J, Richa K, Rostant WG, Farhan Ul Haque M, Murrell JC, Todd JD. 2019. Methanethiol and dimethylsulfide cycling in Stiffkey Saltmarsh. Front Microbiol 10:1040. doi: 10.3389/fmicb.2019.01040 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16. Lomans BP, van der Drift C, Pol A, Op den Camp HJM. 2002. Microbial cycling of volatile organic sulfur compounds. Cell Mol Life Sci 59:575–588. doi: 10.1007/s00018-002-8450-6 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17. Lomans BP, Smolders A, Intven LM, Pol A, Op D, Van Der Drift C. 1997. Formation of dimethyl sulfide and methanethiol in anoxic freshwater sediments. Appl Environ Microbiol 63:4741–4747. doi: 10.1128/aem.63.12.4741-4747.1997 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18. Xu X, Bingemer HG, Georgii H ‐W., Schmidt U, Bartell U. 2001. Measurements of carbonyl sulfide (COS) in surface seawater and marine air, and estimates of the air-sea flux from observations during two Atlantic cruises. J Geophys Res 106:3491–3502. doi: 10.1029/2000JD900571 [DOI] [Google Scholar]
- 19. Kettle AJ, Rhee TS, von Hobe M, Poulton A, Aiken J, Andreae MO. 2001. Assessing the flux of different volatile sulfur gases from the ocean to the atmosphere. J Geophys Res 106:12193–12209. doi: 10.1029/2000JD900630 [DOI] [Google Scholar]
- 20. Kiene RP, Linn LJ, González J, Moran MA, Bruton JA. 1999. Dimethylsulfoniopropionate and methanethiol are important precursors of methionine and protein-sulfur in marine bacterioplankton. Appl Environ Microbiol 65:4549–4558. doi: 10.1128/AEM.65.10.4549-4558.1999 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21. Gould WD, Kanagawa T. 1992. Purification and properties of methyl mercaptan oxidase from thiobacillus-thioparus TK-M. Journal of General Microbiology 138:217–221. doi: 10.1099/00221287-138-1-217 [DOI] [Google Scholar]
- 22. Suylen GMH, Large PJ, Vandijken JP, Kuenen JG. 1987. Methyl mercaptan oxidase, a key enzyme in the metabolism of methylated sulfur-compounds by hyphomicrobium EG. J Gen Microbiol 133:2989–2997. [Google Scholar]
- 23. Schäfer H, Eyice Ö. 2019. Microbial cycling of methanethiol. Curr Issues Mol Biol 33:173–182. doi: 10.21775/cimb.033.173 [DOI] [PubMed] [Google Scholar]
- 24. Porat A, Sagiv Y, Elazar Z. 2000. A 56-kDa selenium-binding protein participates in intra-golgi protein transport. J Biol Chem 275:14457–14465. doi: 10.1074/jbc.275.19.14457 [DOI] [PubMed] [Google Scholar]
- 25. Ishida T, Ishii Y, Yamada H, Oguri K. 2002. The induction of hepatic selenium-binding protein by aryl hydrocarbon (Ah)-receptor ligands in rats. J Health Sci 48:62–68. doi: 10.1248/jhs.48.62 [DOI] [Google Scholar]
- 26. Dervisi I, Valassakis C, Koletti A, Kouvelis VN, Flemetakis E, Ouzounis CA, Roussis A. 2023. Evolutionary aspects of selenium binding protein (SBP). J Mol Evol 91:471–481. doi: 10.1007/s00239-023-10105-4 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 27. Pol A, Renkema GH, Tangerman A, Winkel EG, Engelke UF, de Brouwer APM, Lloyd KC, Araiza RS, van den Heuvel L, Omran H, Olbrich H, Oude Elberink M, Gilissen C, Rodenburg RJ, Sass JO, Schwab KO, Schäfer H, Venselaar H, Sequeira JS, Op den Camp HJM, Wevers RA. 2018. Mutations in SELENBP1, encoding a novel human methanethiol oxidase, cause extraoral halitosis. Nat Genet 50:120–129. doi: 10.1038/s41588-017-0006-7 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28. Philipp TM, Will A, Richter H, Winterhalter PR, Pohnert G, Steinbrenner H, Klotz LO. 2021. A coupled enzyme assay for detection of selenium-binding protein 1 (SELENBP1) methanethiol oxidase (MTO) activity in mature enterocytes. Redox Biol 43:101972. doi: 10.1016/j.redox.2021.101972 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29. Reisch CR, Moran MA, Whitman WB. 2011. Bacterial catabolism of dimethylsulfoniopropionate (DMSP). Front Microbiol 2:172. doi: 10.3389/fmicb.2011.00172 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30. Wang TQ, Yang YQ, Liu MH, Liu HL, Liu HW, Xia YZ, Xun LY. 2022. Elemental sulfur inhibits yeast growth via producing toxic sulfide and causing disulfide stress. Antioxidants (Basel) 11:576. doi: 10.3390/antiox11030576 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31. Hou NK, Yan ZZ, Fan KL, Li HJ, Zhao R, Xia YZ, Xun LY, Liu HW. 2019. OxyR senses sulfane sulfur and activates the genes for its removal in Escherichia coli. Redox Biol 26:101293. doi: 10.1016/j.redox.2019.101293 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32. Toohey JI. 2011. Sulfur signaling: is the agent sulfide or sulfane Anal Biochem 413:1–7. doi: 10.1016/j.ab.2011.01.044 [DOI] [PubMed] [Google Scholar]
- 33. Yadav PK, Yamada K, Chiku T, Koutmos M, Banerjee R. 2013. Structure and kinetic analysis of H2S production by human mercaptopyruvate sulfurtransferase. J Biol Chem 288:20002–20013. doi: 10.1074/jbc.M113.466177 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34. Jiao NZ, Zhang Y, Zeng YH, Hong N, Liu RL, Chen F, Wang PX. 2007. Distinct distribution pattern of abundance and diversity of aerobic anoxygenic phototrophic bacteria in the global ocean. Environ Microbiol 9:3091–3099. doi: 10.1111/j.1462-2920.2007.01419.x [DOI] [PubMed] [Google Scholar]
- 35. Wang P, Cao HY, Chen XL, Li CY, Li PY, Zhang XY, Qin QL, Todd JD, Zhang YZ. 2017. Mechanistic insight into acrylate metabolism and detoxification in marine dimethylsulfoniopropionate-catabolizing bacteria. Mol Microbiol 105:674–688. doi: 10.1111/mmi.13727 [DOI] [PubMed] [Google Scholar]
- 36. Bullock HA, Reisch CR, Burns AS, Moran MA, Whitman WB. 2014. Regulatory and functional diversity of Methylmercaptopropionate coenzyme A Ligases from the dimethylsulfoniopropionate demethylation pathway in DSS-3 and other proteobacteria. J Bacteriol 196:1275–1285. doi: 10.1128/JB.00026-14 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 37. Kim SJ, Shin HJ, Kim YC, Lee DS, Yang JW. 2000. Isolation and purification of methyl mercaptan oxidase from Rhodococcus rhodochrous for mercaptan detection. Biotechnol Bioprocess Eng 5:465–468. doi: 10.1007/BF02931949 [DOI] [Google Scholar]
- 38. Kimura H. 2015. Signaling molecules: hydrogen sulfide and polysulfide. Antioxid Redox Signal 22:362–376. doi: 10.1089/ars.2014.5869 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39. Ran MX, Wang TQ, Shao M, Chen ZG, Liu HW, Xia YZ, Xun LY. 2019. Sensitive method for reliable quantification of sulfane sulfur in biological samples. Anal Chem 91:11981–11986. doi: 10.1021/acs.analchem.9b02875 [DOI] [PubMed] [Google Scholar]
- 40. Filipovic MR, Zivanovic J, Alvarez B, Banerjee R. 2018. Chemical biology of H2S signaling through persulfidation. Chem Rev 118:377–461. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41. Roy B, Shieh M, Ramush G, Xian M. 2023. Organelle-targeted fluorescent probes for sulfane sulfur species. Antioxidants (Basel) 12:590. doi: 10.3390/antiox12030590 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 42. Kimura Y, Koike S, Shibuya N, Lefer D, Ogasawara Y, Kimura H. 2017. 3-Mercaptopyruvate sulfurtransferase produces potential redox regulators cysteine- and glutathione-persulfide (Cys-SSH and GSSH) together with signaling molecules H2S2, H2S3 anDH2S. Sci Rep 7:10459. doi: 10.1038/s41598-017-11004-7 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 43. Ida T, Sawa T, Ihara H, Tsuchiya Y, Watanabe Y, Kumagai Y, Suematsu M, Motohashi H, Fujii S, Matsunaga T, Yamamoto M, Ono K, Devarie-Baez NO, Xian M, Fukuto JM, Akaike T. 2014. Reactive cysteine persulfides and S-polythiolation regulate oxidative stress and redox signaling. Proc Natl Acad Sci U S A 111:7606–7611. doi: 10.1073/pnas.1321232111 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 44. Chauvin JPR, Griesser M, Pratt DA. 2017. Hydropersulfides: H-atom transfer agents par excellence. J Am Chem Soc 139:6484–6493. doi: 10.1021/jacs.7b02571 [DOI] [PubMed] [Google Scholar]
- 45. Sawa T, Takata T, Matsunaga T, Ihara H, Motohashi H, Akaike T. 2022. Chemical biology of reactive sulfur species: hydrolysis-driven equilibrium of polysulfides as a determinant of physiological functions. Antioxidants & Redox Signaling 36:327–336. doi: 10.1089/ars.2021.0170 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 46. Kimura H. 2021. Hydrogen sulfide (H2S) and polysulfide (H2Sn) signaling: the first 25 years. Biomolecules 11:896. doi: 10.3390/biom11060896 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 47. Shimizu T, Ida T, Antelo GT, Ihara Y, Fakhoury JN, Masuda S, Giedroc DP, Akaike T, Capdevila DA, Masuda T, Dupont C. 2023. Polysulfide metabolizing enzymes influence SqrR-mediated sulfide-induced transcription by Impacting intracellular polysulfide dynamics. PNAS Nexus 2:pgad048. doi: 10.1093/pnasnexus/pgad048 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 48. Cao Q, Liu X, Wang Q, Gao W, Xu W, Xia Y, Qin Q, Xun L, Liu H. 2023. Heterotrophic bacteria dominate the sulfide oxidation process in Coastal sediments. Environ Technol Innov 32:103450. doi: 10.1016/j.eti.2023.103450 [DOI] [Google Scholar]
- 49. Schäfer A, Tauch A, Jäger W, Kalinowski J, Thierbach G, Pühler A. 1994. Small mobilizable multipurpose cloning vectors derived from the Escherichia-coli plasmids Pk18 and Pk19 - selection of defined deletions in the chromosome of corynebacterium-glutamicum. Gene 145:69–73. doi: 10.1016/0378-1119(94)90324-7 [DOI] [PubMed] [Google Scholar]
- 50. Harighi B. 2009. Genetic evidence for CheB- and CheR-dependent chemotaxis system in A. tumefaciens toward acetosyringone. Microbiol Res 164:634–641. doi: 10.1016/j.micres.2008.11.001 [DOI] [PubMed] [Google Scholar]
- 51. Xia YZ, Chu WQ, Qi QS, Xun LY. 2015. New insights into the quikchange (TM) process guide the use of phusion DNA polymerase for site-directed mutagenesis. Nucleic Acids Res 43:e12. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 52. Bartlett JK, Skoog DA. 1954. Colorimetric determination of elemental sulfur in hydrocarbons. Anal Chem. 26:1008–1011. doi: 10.1021/ac60090a014 [DOI] [Google Scholar]
- 53. Li HJ, Liu HW, Chen ZG, Zhao R, Wang QD, Ran MX, Xia YZ, Hu X, Liu JH, Xian M, Xun LY. 2019. Using resonance synchronous spectroscopy to characterize the reactivity and electrophilicity of biologically relevant sulfane sulfur. Redox Biol 24:101179. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 54. Xin Y, Liu H, Cui F, Liu H, Xun L. 2016. Recombinant Escherichia coli with sulfide:quinone oxidoreductase and persulfide dioxygenase rapidly oxidises sulfide to sulfite and thiosulfate via a new pathway. Environ Microbiol 18:5123–5136. doi: 10.1111/1462-2920.13511 [DOI] [PubMed] [Google Scholar]
- 55. Lu T, Wu X, Cao Q, Xia Y, Xun L, Liu H, Dahl C, Harwood CS. 2022. Sulfane sulfur posttranslationally modifies the global regulator AdpA to influence actinorhodin production and morphological differentiation of Streptomyces coelicolor. mBio 13. doi: 10.1128/mbio.03862-21 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 56. Lu T, Cao Q, Pang XH, Xia YZ, Xun LY, Liu HW. 2020. Sulfane sulfur-activated actinorhodin production and sporulation is maintained by a natural gene circuit in Streptomyces coelicolor. Microb Biotechnol 13:1917–1932. doi: 10.1111/1751-7915.13637 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 57. Jumper J, Evans R, Pritzel A, Green T, Figurnov M, Ronneberger O, Tunyasuvunakool K, Bates R, Žídek A, Potapenko A, et al. 2021. Highly accurate protein structure prediction with alphafold. Nature 596:583–589. doi: 10.1038/s41586-021-03819-2 [DOI] [PMC free article] [PubMed] [Google Scholar]
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Supplementary Materials
Methods, Tables S1 and S2, and Figures S1-S17.







