Desulfovibrio vulgaris as a model microbe for the study of corrosion under sulfate-reducing conditions
Edited by Hailiang Dong, Miami University, USA
Abstract
Corrosion of iron-containing metals under sulfate-reducing conditions is an economically important problem. Microbial strains now known as Desulfovibrio vulgaris served as the model microbes in many of the foundational studies that developed existing models for the corrosion of iron-containing metals under sulfate-reducing conditions. Proposed mechanisms for corrosion by D. vulgaris include: (1) H2 consumption to accelerate the oxidation of Fe0 coupled to the reduction of protons to H2; (2) production of sulfide that combines with ferrous iron to form iron sulfide coatings that promote H2 production; (3) moribund cells release hydrogenases that catalyze Fe0 oxidation with the production of H2; (4) direct electron transfer from Fe0 to cells; and (5) flavins serving as an electron shuttle for electron transfer between Fe0 and cells. The demonstrated possibility of conducting transcriptomic and proteomic analysis of cells growing on metal surfaces suggests that similar studies on D. vulgaris corrosion biofilms can aid in identifying proteins that play an important role in corrosion. Tools for making targeted gene deletions in D. vulgaris are available for functional genetic studies. These approaches, coupled with instrumentation for the detection of low concentrations of H2, and proven techniques for evaluating putative electron shuttle function, are expected to make it possible to determine which of the proposed mechanisms for D. vulgaris corrosion are most important.
INTRODUCTION
Understanding the mechanisms for the corrosion of metals is key to developing strategies for preventing this economically significant problem1, 2. Following the first suggestion that microbes might be important catalysts for the corrosion of metals3, 4, a thorough analysis of the available data led to the conclusion that sulfate-reducing microorganisms play a key role in iron corrosion5. However, in the 1930s, Spirillium desulfuricans was the only microbe known to be capable of sulfate reduction5. The genus and species names of this and similar strains of sulfate-reducing bacteria investigated in corrosion studies have changed over time6, 7, but most are now generally recognized as strains of Desulfovibrio vulgaris (Table 1).
Year | Straina | Iron source | Lactate | Mechanismb | Reference |
---|---|---|---|---|---|
1934 | Spirillum desulfuricans | CI | + | Ha | 5 |
1939 | Vibrio desulfuricans | MS | + | N | 8 |
1947 | Vibrio desulfuricans | MS | − | N | 9 |
1951 | Vibrio desulfuricans | Armco ingot iron | + − |
Ha | 10 |
1952 | Vibrio desulfuricans | Armco ingot iron | + − |
S | 11 |
1960 | D. desulphuricans Hildenborough NCIB 8303 | MS | + | Ha | 12 |
1964 | D. desulphuricans Benghazi NCIB 8401 | MS | +? | Ha | 13 |
America NCIB 8372 | |||||
Teddington R NCIB 8312 | |||||
Hildenborough NCIB 8303 | |||||
Llanelly NCIB 8446 | |||||
1968 | D. desulfuricans Teddington R | MS | + | S | 14 |
1968 | Hildenborough NICB 8303 | MS | + | Ha | 15 |
1971 | D. desulfuricans Teddington R NCIB 8312 | MS | + − (+F) |
Hs | 16 |
1974 | Hildenborough NCIB 8303 | MS | + | S | 17 |
1982 | Isolated from River Thames' sediment | MS (EN2) | + | N | 18 |
1986 | Hildenborough NCIB 8303 | MS | − (+A) | Ha | 19 |
1986 | Marburg DSM 2119 (Postgate and Campbell) | Steel | + − (+A) |
Ha | 20 |
1986 | Madison | MS | − (+F) | Ha | 21 |
1990 | Hildenborough NCIB 8303 | MS | + | Ha | 22 |
1991 | DSM 1744 (Postgate and Campbell) | SS (AISI 3161) | − | N | 23 |
1991 | Not specified | Iron (99%) SS (Fe–15Cr–10Ni) | + | Hs | 24 |
1991 | Not specified | SS (410) | + | S | 25 |
1991 | Isolated from cutting oil emulsions | CS (SAE 1020) | + | N | 26 |
1992 | Woolwich NCIMB 8457 | MS (BS970) | + | N | 27 |
1993 | NCIB 8303 | Iron | + | N | 28 |
(Postgate and Campbell) | CS (SAE 1090) | ||||
(Hildenborough) | SS (18-8) | ||||
(DSM 644) | |||||
1994 | Not specified | CS (X52) | − | N | 29 |
1995 | Isolated from cutting oil emulsions | MS | + | N | 30 |
1995 | Not specified | SS (304) | + | N | 31 |
1995 | ATCC 25979 | SS (304) | + | N | 32 |
1997 | Not specified | SS (AISI 304L) | + | N | 33 |
1997 | Not specified | SS (316L) | + | N | 34 |
1999 | ATCC 29579 | MS (SAE 1018) | + | N | 35 |
(Postgate and Campbell) | SS 304 | ||||
(Hildenborough) | |||||
(NCIB 8303, DSM 644) | |||||
2002 | LMG 7563 | MS | + | N | 36 |
2004 | Not specified | Iron | − (+A) | D | 37 |
2004 | ATCC 29579 | MS (1010) | + | N | 38 |
2007 | DSM 664 | MS (BST 503-2) | + | N | 39 |
2008 | Hildenborough NCIMB 8303 | CS (ASTM A366) | + − (+A) |
Ha | 40 |
2008 | Isolated from an oil field separator | MS (AISI 1018) | − | N | 41 |
2008 | DSMZ 644 | Iron | + | N | 42 |
CS (ST 37) | |||||
SS (304) | |||||
2010 | DSMZ 644 | Alloyed steel (1.4301, UNS 304) | + | N | 43 |
2013 | ATCC 7757 | CS (C1018) | + | N | 44 |
(Postgate and Campbell) | |||||
(C-6, CT1, IFO 13699, NCIB 8372) | |||||
2014 | ATCC 7757 | CS (C1018) | + | N | 45 |
2014 | ATCC 7757 | CS (X70) | + | N | 46 |
2014 | ATCC 7757 | CS (API5L X-70) | + | N | 47 |
2014 | ATCC 7757 | CS (API5L-X70) | + | N | 48 |
2015 | ATCC 7757 | CS (C1018) | + | F | 49 |
2015 | ATCC 7757 | SS (304) | + | F | 50 |
2016 | ATCC 7757 | CS (C1018) | + | N | 51 |
2016 | ATCC 7757 | CS (UNS G10100) | + | N | 52 |
2016 | Hildenborough DSM 644 | MS (BST 503-2) | + | N | 53 |
2017 | Not specified | CI | + | N | 54 |
2017 | ATCC 7757 | MS | + | N | 55 |
2017 | ATCC 7757 | CS (C1018) | + | N | 56 |
2018 | ATCC 7757 | CS (C1018) | + | S | 57 |
2019 | Not specified | CS (1018) | + | N | 58 |
2019 | ATCC 7757 | CS (1018) | + | N | 59 |
2019 | ATCC 7757 | PS (X80) | + | N | 59 |
2020 | Hildenborough | CS (1030) | + | N | 60 |
2020 | ATCC 7757 | SS (2205) | + | N | 61 |
2020 | Hildenborough | CS | + | N | 62 |
2020 | ATCC 7757 | CS (X65) | + | F | 63 |
2021 | ATCC 7757 | GS | + | N | 64 |
2021 | ATCC 7757 | SS (410, 420, 316, 2206) | + | N | 65 |
2021 | ATCC 7757 | CS (C1018) | + | N | 66 |
2021 | ATCC 7757 | SS (2205) | + | N | 67 |
2021 | ATCC 7757 | SS (2205) | + | N | 68 |
- a Strains now considered to be Desulfovibrio vulgaris were previously designated as Spirillium desulfuricans, Vibrio desulfuricans, Desulfovibrio desulfuricans, and Desulfovibrio desulphuricans6, 7. Therefore, microbes that were later renamed D. vulgaris are listed by the name designated in the original text. Only strain designations are listed for strains designated as D. vulgaris in the original text. Alternative designations for these strains are described in parentheses.
- b Primary corrosion mechanism discussed. Ha, abiotic H2 production from iron; Hs, H2 production from iron-catalyzed by FeS mineral deposits; S, sulfide promoting iron corrosion; D, direct electron transfer; F, electron transfer with a flavin shuttle; N, not applicable (the studies focused on biofilm formation, growth inhibition, corrosion inhibition, etc.). +, lactate included; −, no lactate; − (+A), no lactate but acetate added; − (+F), cells grown on fumarate; CI, cast iron; CS, carbon steel; GS, galvanized steel; MS, mild steel; PP, pipeline steel; SS, stainless steel.
There is substantial evidence that Desulfovibrio species are involved in the corrosion of iron-containing metals in anaerobic environments69, 70. Desulfovibrio species were abundant within the microbial community on metal surfaces exposed to oil field production waters71, 72, corroded oil pipelines73, corroding steel pipe carrying oily seawater74, rust layers on steel plates immersed in seawater75, and the inner rust layer on carbon steel76. Desulfovibrio species were recovered in culture from corrosion sites77-80, including a D. vulgaris strain isolated from an oil field separator in the Gulf of Mexico that was damaged by corrosion41. Microbial activity on the cathodes of bioelectrochemical systems is thought to be related to microbial corrosion81 and Desulfovibrio species are often enriched on cathodes from diverse microbial communities82-84.
Several mechanisms for D. vulgaris corrosion of iron-containing metals have been proposed (Figure 1). These mechanisms may not be mutually exclusive. As detailed in this review, each of these models still requires rigorous examination. However, with the increasing availability of molecular tools to probe microbial activity and tools for genetic manipulation of D. vulgaris85, 86, it now may be the time to either eliminate or confirm some of the existing mechanistic models for D. vulgaris corrosion or to develop new models. The purpose of this review is to summarize the previously proposed routes for Desulfovibrio species iron corrosion and to suggest experimental approaches to further advance the understanding of corrosion by this popular model microbe.

IRON CORROSION VIA AN H2 INTERMEDIATE
and growth on H2 is possible if acetate is provided as a carbon source87.
Substantial abiotic H2 production from Fe0 was discounted in the early version of the model in which H2 serves as an electron carrier between Fe0 and cells5. However, the mechanism by which cells promoted the oxidation of Fe0 with the production of H2 was not specified. It is now known that the extent of abiotic H2 production depends upon the form of the iron-containing metal. For example, pure Fe0 abiotically produces substantial H2 when submerged in anoxic water at circumneutral pH whereas 316 stainless steel does not88, 89.
This difference in H2 production between Fe0 and stainless steel could provide one method for evaluating whether D. vulgaris relies on H2 production to consume electrons from iron-containing metals. The closely related sulfate reducer D. ferrophilus reduced sulfate when pure Fe0 was the electron donor, but not in a medium with stainless steel90. In contrast, Geobacter species capable of direct electron uptake could use either iron form as an electron donor88-90. These results indicated that D. ferrophilus was incapable of direct electron uptake and required the production of H2 to mediate electron transfer between Fe0 and cells.
The most direct approach to evaluating whether H2 is an important intermediate in electron uptake from extracellular electron donors may be to generate a mutant that is unable to consume H291. D. vulgaris Hildenborough has multiple hydrogenases that have different localizations and metal constituents: the periplasmic [NiFe] HynAB-1 and HynAB-2, the periplasmic [Fe] HydAB, the periplasmic [NiFeSe] HysAB, the cytoplasmic [Fe] HydC, and the cytoplasmic membrane-bound Coo and Ech hydrogenases92. Deletions of genes for HydAB, HynAB-1, or HysAB negatively impacted the growth of D. vulgaris Hildenborough with H2 as the electron donor93-95. However, these single-gene deletion mutants and a double deletion mutant of HynAB-1 and HydAB95 still grew on H2 as the electron donor, indicating redundant, complementary functions of the multiple hydrogenases. Thus, the construction of a strain with multiple hydrogenase gene deletions may be required to rigorously evaluate the role of H2 in corrosion.
Transcriptomic analysis comparing growth on H2 supplied from proton reduction with an iron electrode poised at −1.1 V versus growth on H2 simply bubbled into medium revealed that the genes for HynAB-1 and HydAB were more highly expressed during growth on the cathodic H240. Gene transcripts for HysAB were more abundant when H2 was bubbled into the medium. Gene deletions that prevented the function of the HynAB-1 and HydAB hydrogenases inhibited electron uptake from the iron cathodes40, as might be expected for cathodes poised at a low potential to induce H2 production. The impact of the hydrogenase gene deletions on corrosion of iron that was not artificially poised at a negative potential was not determined because wild-type cells could not be grown under these conditions40. Lack of growth on unpoised iron suggests an inability to use Fe0 as an electron donor. This difference between artificially poised iron cathodes and unpoised iron metal is an important consideration when evaluating other studies19 that have concluded that H2 is an important intermediate in iron corrosion by D. vulgaris based on experiments with electrochemically poised iron electrodes.
However, there is some indirect evidence for H2 serving as an intermediary electron carrier between Fe0 and D. vulgaris, especially when H2 is not the sole electron donor. D. vulgaris did not reduce sulfate when steel wool was provided as the sole electron donor, but when lactate was added as an additional electron donor, more sulfide was produced than was possible from lactate oxidation alone20. In contrast, D. sapovorans, which cannot utilize H2, did not produce substantially more sulfide when grown in the presence of lactate and steel wool, than when grown with lactate alone. These results suggested that H2 was an intermediary electron carrier for D. vulgaris electron uptake from the steel wool during growth with lactate20. The expression of one or more uptake hydrogenases is expected to be upregulated when H2 is serving as an electron donor96-98. Thus, transcriptional and/or proteomic studies may be useful in further assessing the role of H2 as an electron donor during corrosion in the presence of lactate. Additional indirect evidence for the importance of H2 as an electron carrier was the finding that D. vulgaris corroded “mild steel” faster than the gram-positive D. orientis, which cannot consume H212, 13.
Other early studies suggested that H2 production from iron was not a mechanism for corrosion10, 11. However, the medium for investigating the possibility for H2 serving as an electron donor did not include acetate, which is required as a carbon source for growth on H2. Therefore, no conclusion on the role of H2 is possible from those studies.
FACTORS PROMOTING H2 PRODUCTION
In a diversity of microbes, hydrogenases released from lysed cells, or specifically transported to the outer surface of living cells, facilitate the production of H2 from Fe099-102. For example, methanogens highly effective in corrosion can produce an extracellular hydrogenase that enhances H2 production from Fe099. Such extracellular hydrogenases have not been reported in Desulfovibrio species, but moribund cells of D. vulgaris release periplasmic hydrogenases that can retain activity for months103. Subjecting D. vulgaris to starvation, a condition likely to promote cell death and lysis, enhanced corrosion45, 58. Therefore, studies to evaluate the role of extracellular hydrogenases in corrosion by D. vulgaris are warranted.
The iron sulfide that precipitates on iron-containing metals during corrosion coupled to sulfate reduction may also increase H2 production. The addition of FeS reduced the overpotential necessary to produce H2 from iron cathodes, suggesting a role for FeS in promoting the formation of H216. In studies in which the culture was grown on fumarate rather than via sulfate reduction, the current was generated at more positive potentials when FeS was deposited on either mild steel or platinum cathodes14. These results further indicate that FeS may serve as a catalyst for H2 generation. However, in studies with carbon steel coupons, it appeared that higher accumulations of sulfide inhibited corrosion57. The ability of D. vulgaris to corrode steel with either benzyl viologen as the electron acceptor15 or when growing on fumarate21 demonstrated that sulfide production was not essential for corrosion. Thus, a clear-cut concept for the role of FeS in corrosion has yet to be established.
Technology for measuring H2 concentrations at extremely low concentrations during corrosion is available89. Thus, with the appropriate H2 detector it should be possible to directly evaluate the role of FeS in facilitating H2 production from iron-containing metals, simply by monitoring H2 generation in the presence or absence of different quantities of FeS precipitate.
ELECTRON SHUTTLES OTHER THAN H2
Soluble redox-active molecules promote extracellular electron exchange between microbes and minerals, electrodes, and other microbial species104-107. These electron shuttles typically accelerate extracellular electron exchange by alleviating the need for outer-surface electron transfer components to establish direct electrical contact with particulate extracellular donors and acceptors. The addition of riboflavin and flavin adenine dinucleotide enhanced D. vulgaris corrosion of carbon steel and stainless steel49, 50, 63. However, amendments of these cofactors, which are important for the function of numerous proteins, could influence D. vulgaris growth and metabolism in many ways. To determine whether flavins can serve as an electron shuttle for the corrosion of iron-containing metals coupled to sulfate reduction it is necessary to demonstrate that: (1) the metals are capable of reducing the flavins; and (2) that the reduced flavins can serve as electron donors for sulfate reduction.
DIRECT ELECTRON UPTAKE
Direct electron uptake from iron-containing metals has been demonstrated with Geobacter sulfurreducens and Geobacter metallireducens88-90. Strains unable to utilize H2 readily reduced fumarate, nitrate, or Fe(III) with pure Fe0 or stainless steel as the electron donor. Deletion of genes for outer-surface, multiheme c-type cytochromes previously shown to be involved in electron exchange with other extracellular donors/acceptors inhibited the corrosion.
There are no examples of similar studies with sulfate-reducing microorganisms. It was suggested that c-type cytochromes positioned in the outer membrane of D. vulgaris might be able to make an electrical connection with Fe0108. However, subsequent studies have indicated that D. vulgaris does not have outer-surface cytochromes92. Clear next steps in this line of investigation would be to rigorously verify whether cytochromes are exposed on the outer surface of D. vulgaris, and if so, evaluate their role in iron corrosion with the appropriate gene deletion studies. Genetic, biochemical, biophysical, and immunological approaches previously employed for investigating the location and function of the outer-surface cytochromes of Geobacter would be suitable109-112.
Although it has been suggested that several of the c-type cytochromes of D. ferrophilus may be localized in the outer membrane, no genetic studies have been conducted to determine whether they are involved in extracellular electron exchange90, 113-115. As noted above, experimental analysis of iron corrosion by D. ferrophilus has suggested that it relies on H2 as an intermediary electron carrier rather than direct electron uptake90.
CONCLUSIONS AND FUTURE DIRECTIONS
Sulfate-reducing microorganisms are considered to be important agents for catalyzing the corrosion of iron-containing metals and D. vulgaris has historically been the model microbe of choice for elucidating the mechanisms for corrosion by sulfate reducers. As summarized above (Figure 1), previous studies have suggested several mechanisms by which D. vulgaris may enhance corrosion, but each of the proposed mechanisms requires further experimental evaluation. The mechanisms for electron transfer between iron-containing metals and Geobacter species were elucidated with genome-scale transcriptomics coupled with phenotypic analysis of mutant strains in which the genes for proteins hypothesized to be involved in electron transfer were deleted88, 89. Deletion of the genes for hydrogenases and hypothesized outer-surface electrical contacts made it possible to determine the role of H2 as an intermediary electron carrier and to identify likely electrical contacts on the outer surface of the cell. A similar approach seems possible for the study of D. vulgaris corrosion mechanisms. Transcriptomics of D. vulgaris biofilms is possible39, 40 to aid in identifying components that may have increased expression during corrosion of iron-containing metals versus other growth modes. Other candidates for corrosion components may be identified from the known physiological roles of proteins or their cellular location. Methods for the targeted deletion of genes in D. vulgaris are available85, 86 making it possible to evaluate the function of proteins hypothesized to be of importance. In fact, an extensive library of D. vulgaris mutants is publicly available, potentially eliminating the substantial investment of time and resources required for mutant construction86. Comparison of corrosion capabilities with Fe0, which readily reduces protons to generate H2, versus stainless steel, which does not generate H2, provides an additional tool to evaluate the role of H2 as an intermediary electron carrier for corrosion89, 90. Mechanisms for the corrosion of carbon steel, the most common form of iron in structural materials, should also be investigated. The hypothesis that FeS deposits stimulate H2 production from iron-containing metals should be readily addressable with highly sensitive H2 detection systems88, 89. Mechanistic and genetic116-120 approaches for the study of the role of electron shuttles in electron transfer to minerals and electrodes should be applicable to the study of the role of flavins as electron shuttles for corrosion. Therefore, it is expected that D. vulgaris will continue to serve as an important model microbe for the further elucidation of mechanisms for corrosion under sulfate-reducing conditions.