The effect of sulfate-reducing bacteria (SRB) on the corrosion of 907
steel was investigated. Results demonstrated that the chemical composition of
corrosion products, the corrosion rate, and corrosion type were altered due to the
adherence of SRB and the subsequent formation of biofilm on the 907 steel surface.
Different from the case in sterile medium that ferrous oxides predominated in the
corrosion products, ferrous sulfide was an important component in SRB-containing
medium. Meanwhile, corrosion of 907 steel was enhanced by SRB, and the corrosion
rate was dependent on their metabolic activity, which increased, stabilized, and
decreased in the exponential growth, death, and residual phases, respectively.
Furthermore, the corrosion type was changed from uniform corrosion to localized
corrosion with the introduction of SRB, and the development process was analyzed
based on the current distribution map of wire beam electrodes. In sterile medium,
the maximum current density decreased with the immersion time extended, and there
were no significant anodic current peaks in the late period, while in SRB-containing
medium, the ratio between cathodic areas and anodic areas was high in the
exponential growth phase, and stable anodic sites formed gradually in death and
residual phases, which facilitated the development of localized corrosion.
Notes
The original version of this article was revised due to a retrospective Open
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Introduction
Marine environment is a natural habitat for a large variety of
microorganisms, and their attachment to surfaces and formation of slimy biofilm will
affect corrosion behavior of metal facilities, which is termed as microbiologically
influenced corrosion (MIC). MIC is a vital cause for corrosion failure of marine
infrastructures and leads to financial losses of billions of dollars each year (Ref
1). Sulfate-reducing bacteria (SRB),
gaining energy from the oxidation of organic compounds or H2
by the dissimilatory reduction of sulfate or other partially oxidized inorganic
sulfur species to sulfide (Ref 2), have
long been viewed as the most influential members of microorganisms involved in MIC.
Numerous work has been devoted to the influence of SRB on the corrosion of metals
since the first report appeared in 1934 (Ref 3), and so far several mechanisms have been proposed such as
cathodic depolarization by hydrogenase and sulfide (Ref 4), chelation of extracellular polymeric
substances (EPS) toward metal ions (Ref 5), direct electron transfer from Fe0
(Ref 6), and biocatalytic cathodic
sulfate reduction (Ref 7). The validity
of these corrosion mechanisms is dependent on SRB strains, metal material features,
and medium characteristics.
907 steel, a high-strength low-alloy steel, is widely utilized in the
construction of marine ship hulls due to its good mechanical properties and
resistance to corrosion. Most reports have been focused on its galvanic corrosion
coupled with other metals (Ref 8,
9), and little is known about its
corrosion behavior influenced by microorganisms. To be the best of our knowledge,
there has been only one report from Duan et al. (Ref 10) concentrated on 907 steel corrosion affected by microbes.
They covered 907 steel surface with an artificial biofilm consisting of SRB cells
and agar, and found that coupons corroded more severely in nutrient-rich medium than
in natural seawater. Although this work sheds some light on 907 steel corrosion in
the presence of SRB, it suffers several defects such as the absence of control
designs without SRB and the lack of impact from biofilm development process.
Therefore, comprehensive research is highly desirable in this topic.
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MIC is an electrochemical process, and electrochemical methods such as
polarization curve and electrochemical impedance spectroscopy (EIS) are commonly
adopted to investigate the corrosion behavior of metals influenced by
microorganisms. Unluckily, these conventional electrochemical techniques provide
average corrosion information, leaving local electrochemical characteristics
unknown, which is not beneficial for the comprehension of the MIC process that is
recognized as a typical localized corrosion due to the heterogeneity of the biofilm
attached to the surfaces (Ref 11,
12). Although localized
electrochemical methods are highly desirable in MIC study, there are still quite
limited reports on this. The reported techniques include scanning vibrating
electrode (SVT) (Ref 13), local
electrochemical impedance spectroscopy (LEIS) (Ref 14), and wire beam electrode (WBE) (Ref 15). In comparison with SVT, no probe is
involved in WBE, and therefore, it overcomes the problem of the interference from
the probe contamination by biofilm absorption in SVT. In the meanwhile, the analysis
of WBE data is simpler than that of LEIS. Consequently, the WBE method has
advantages over the other two techniques in MIC investigation. In our previous work,
the WBE technique has been employed to study MIC of copper and Q235 carbon steel,
and the current distribution map gives a straightforward indication for the
localized corrosion (Ref 16,
17).
In this study, corrosion of 907 steel was investigated in media with and
without the inoculation of SRB by the combination of surface analysis, conventional
and localized electrochemical methods, and the role of SRB was ascertained.
Furthermore, the corrosion mechanism was discussed in relation to the growth states
of SRB.
Experimental
Materials
Coupons were cut from a piece of 907 steel sheet with the
composition (wt.%) of 0.120 C, 0.790 Si, 1.010 Mn, 0.007 S, 0.420 Cu, 0.050 Ti,
0.640 Cr, 0.670 Ni, 0.016 P, and balance Fe. Cylinders with a diameter of 5.0 mm
and height of 5.0 mm were used for conventional electrochemical measurements and
surface analysis, and they were embedded in epoxy resin to leave only one end
surface (19.6 mm2) exposed to aggressive electrolyte
after copper wires were soldered. A WBE was prepared by the assembly of 112
steel wires (diameter 1.5 mm) into an array of 11 × 11, and the distance between
each wire was 1 mm (Fig. 1a).
×
Prior to electrochemical measurements, the electrode surface was
sequentially abraded with a series of silicon carbide papers with grit sizes of
400, 600, 800, and 1200 #, cleaned by ethanol in ultrasonication bath, dried by
nitrogen, and sterilized by ultraviolet for 30 min.
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Microorganism Cultivation and Growth Curve Measurement
The bacterium identified as Desulfovibrio sp. was isolated from marine sludge in Bohai Sea
of China. The modified Postgate’s culture solution was used as the culture
medium, and it consisted of 2.0 g magnesium sulfate, 0.5 g dipotassium hydrogen
phosphate, 1.0 g ammonium chloride, 0.5 g sodium sulfate, 0.1 g calcium
chloride, 1.0 g yeast extract, and 4.0 ml sodium lactate per liter of seawater.
Culture medium was autoclaved at 121 °C for 20 min. After cooling, SRB seed
culture with the 4-day old was inoculated, and then electrodes and rubber
stopper were assembled rapidly. Figure 1(b) displays the schematic diagram of WBE setup. All the vessels
were kept at 30 °C in a thermostatic incubator.
The quantity of active SRB (NSRB) was detected by the most probable
number (MPN) method according to the American Society for Testing and Materials
(ASTM) Standard D4412-84 (Ref 18).
Surface Morphological and Elemental Analysis
The surface morphology of coupons exposed to media for diverse time
was examined with a scanning electron microscopy (SEM, JSM-6700F; JEOL Ltd.;
Tokyo, Japan). After the samples were taken out from the media and rinsed with
sterilized natural seawater, they were immersed in a phosphate buffer solution
containing 2.5% glutaraldehyde for 2 h to fix the biofilm. And then coupons were
dehydrated successively with an ethanol gradient (15 min each): 30, 50, 70, 90,
and 100%. Subsequently, they were dried at critical point, sputter-coated with
gold, and subjected to SEM analysis. To observe the corrosion morphology beneath
corrosion products and biofilm, the coupons were cleaned with the Clark’s
solution (ASTM G1-03) before SEM characterization.
Chemical composition of 907 steel surface immersed in sterile and
SRB-containing media for 13 days was obtained by x-ray photoelectron
spectroscopy (XPS, Thermo ESCALAB 250, Waltham, MA, USA). The C 1 s hydrocarbon
peak was calibrated at a binding energy of 285.0 eV. Peak fitting was performed
using software XPS Peak-fit 4.1.
Electrochemical Experiments
Open-circuit potential (EOC) and EIS experiments were performed
on a CHI604D station (CH Instruments, Inc.; Texas, USA) with a three-electrode
system, in which an Ag/AgCl (KCl-sat.) and a platinum wire were used as
reference and counter electrodes, respectively. EIS studies were carried out at
EOC using a 5 mV
amplitude sinusoidal signal with a frequency range of
10−2 to 105 Hz, and
the data were fitted with ZSimpWin software.
Similar to those reported in the literature, the current
distribution of WBE was measured using a test device (NI PXI-1042Q) consisting
of NI PXI-8108 embedded controller and modular instruments: NI PXI-2535,
PXI-4022, and PXI-4071 (Ref 16).
After a WBE was immersed in media, all wire sensors were connected to allow
electrons to move freely among wires. When current was recorded, each individual
wire was separated temporarily from the wire array in sequence, and all the
other wires were shorted together. The galvanic current between the temporarily
separated wire and the residual wires was recorded by PXI-4071 and PXI-4022. All
measurement processes were controlled via a self-designed program in LabVIEW
environment. During the current measurements, the interval between two channels
was 1 s. The current distribution maps were drawn with the Surfer 10.0
software.
Results and Discussion
The Growth Curve of SRB
Figure 2 displays the
growth curve of SRB, which can be divided into three stages: an exponential
phase, a death phase, and a residual phase. In the first 3 days, NSRB increased
exponentially, and then decayed quickly. Bacteria are highly active in the
exponential stage (Ref 19-21), and there is a high rate of nutrient consumption and
metabolite accumulation. For the present bath culture model, the consumption of
nutrients and accumulation of metabolites restricted the further increase in SRB
quantity and promoted their decay, which occurred from the third day. After the
11th day, the nutrients in the medium were almost exhausted, and the growth
process reached the third stage. During the residual phase, NSRB went back to the
original level, and the active cells almost disappeared.
×
Surface Morphological and Elemental Analysis
SEM images of 907 steel exposed to sterile and SRB-containing media
for different times are shown in Fig. 3.
In sterile medium, a small amount of corrosion products dispersed randomly on
the surface at the time of 2 h, and scratch lines from the pretreatment were
clearly observed. When the exposure time extended to 1 day, the morphology did
not change significantly except for a slight increase in the number and size of
corrosion product particles. Subsequently, a thin film began to cover the
surface at the third day, and the scratch lines became blurred. After 13 days of
immersion, a dense layer with several small humps was formed on the 907 steel
surface.
×
Distinct from the samples in sterile medium, bacteria and their EPS
accumulated gradually on the surface with increasing the exposure time in
SRB-containing medium. Small loose aggregates mainly composed of EPS appeared on
the surface after 2 h of immersion and quite few bacterial cells were observed.
The size of aggregates increased when the exposure time rose to 1 day, and in
the meanwhile, the quantity of attached SRB cells grew. EPS accumulated rapidly
on the surface during the exponential stage from day 1 to day 3 due to the
vigorous metabolic activity of SRB, which facilitated the adherence of bacterial
cells. The attached SRB cells, in turn, benefited the further accumulation of
EPS. As a result, 907 steel was totally covered by a thick film consisting of
EPS and bacterial cells on the third day. Although the planktonic SRB decayed
from the third day, there were still a few cells present in the film on the 13th
day. Long-term survival of SRB on steel surface is in good agreement with the
report by Chen et al. (Ref 22).
Figure 4 exhibits SEM
images of 907 steel substrates after the removal of biofilm and corrosion
products. After 13 days of immersion, samples in sterile medium suffered slight
and uniform damage, while the corrosion of coupons in the medium containing SRB
was worse and severe pits with different diameters were distributed unevenly on
the surface. Consequently, the presence of SRB resulted in localized corrosion
of 907 steel.
×
The presence of SRB altered the corrosion morphology of 907 steel,
and their influence on the chemical composition of corrosion products was
further investigated by XPS, and the results are displayed in Fig. 5. As shown, characteristic peaks for Fe, S, C,
N, and O elements were observed on the wide spectra of coupons exposed to
sterile and SRB-containing media. In comparison with the case in sterile medium,
the proportion of element S in the sample from SRB-containing medium was much
higher, indicating that sulfide from metabolism of SRB participated in the
corrosion process of 907 steel.
×
Figure 6 depicts the
high-resolution Fe 2p3/2 and S 2p spectra of samples after 13 days of immersion in both media,
and their deconvolution was achieved by the curve-fitting procedure using the
Peak-Fit 4.1 software. The Fe 2p3/2 spectrum in the sterile medium could
be divided into three peaks at the position of 710.4, 711.8, and 713.0 eV,
corresponding to FeO, Fe3O4, and
FeSO4, respectively (Ref 23-26).
Fe3O4 generated via Schikorr
reaction is common in the anaerobic corrosion of iron and carbon steel (Ref
27). The relative content of
each component is summarized in Table 1,
and the proportions of FeO, Fe3O4,
and FeSO4 were 60.02, 32.45, and 7.53%, respectively.
Therefore, iron oxides predominated the corrosion products in sterile medium.
The Fe 2p3/2 spectrum
in SRB-containing medium also consisted of three peaks, and the peak at 710.6 eV
could be assigned to FeS, a typical corrosion product induced by SRB (Ref
28). Furthermore, the high
proportion of FeS (46.91%) indicated that the metabolic activity of SRB resulted
in a transformation from iron oxides to iron sulfides.
Table 1
Relative peak area of Fe and S compounds of 907 steel in
culture medium without and with SRB for 13 days
Component
Position, eV
Area
(%)
Sterile-Fe 2p
3/2
FeO
710.400
1084.249
60.02
Fe3O4
711.800
586.221
32.45
FeSO4
713.000
136.011
7.53
SRB-Fe 2p 3/2
FeS
710.600
4050.432
46.91
Fe3O4
711.800
2590.234
30.00
FeSO4
713.000
1993.248
23.09
Sterile-S
2p
Org-S
162.600
254.117
49.69
Org-S
163.700
134.867
26.37
SO42−
167.200
122.466
23.94
SRB-S 2p
FeS
161.200
1135.009
48.46
FeS
162.200
441.250
18.84
Org-S
162.600
472.329
20.16
Org-S
163.700
293.658
12.54
×
Figure 6(c) exhibits the
high-resolution S 2p spectrum for the coupon
in sterile medium. Peaks at 162.6 and 163.7 eV were ascribed to the adsorbed
organic sulfur-containing compounds (Org-S) from culture solution, and the other
at 167.2 eV corresponds to SO42− (Ref 29, 30). According to the result in
Table 1, most sulfur was present in
the form of Org-S (76.06%). When SRB cells were inoculated, besides the two
peaks for Org-S, another two appeared at the position of 161.2 and 162.2 eV.
These two peaks could be attributed to FeS (Ref 31), which is in accordance with the result displayed in
Fig. 6(b). Meanwhile, FeS gave a
proportion of 67.30% in the total sulfur.
Thus, the adherence of SRB on 907 steel surface altered the
corrosion type and chemical composition of corrosion products, leading to severe
localized corrosion and the generation of FeS.
Evolution of EOC
and EIS
Figure 7 illustrates the
variation of EOC with
respect to time in sterile and SRB-containing media. It could be seen that the
value of EOC shifted
positively at the beginning of the experiment, and then started to stabilize
from the fourth day in sterile medium. The gradual accumulation of corrosion
products on the surface hampered the diffusion of corrosive species toward the
steel substrate, and accordingly protected the coupon against further corrosion.
In SRB-containing medium, EOC of 907 steel was more negative than
that in sterile medium, and it varied with the growth states of SRB. In the
exponential growth period (1-3 days), EOC decreased rapidly and reached a
minimum value. This was closely related to the sulfide from bacterial
metabolism, which accelerated the metal dissolution process (Ref 32). There was a slight positive shift of
EOC during the
death period, and the formation of biofilm on 907 steel played a key role in the
ennoblement (Ref 33-35).
EOC keeps stable
in the residual period, which might be associated with the reduction in the
biological activity of bacteria and the deposition of corrosion products.
×
Figure 8 shows Nyquist
plots of 907 steel in sterile and SRB-containing media for different times. In
the sterile medium, there were only impedance loops in the plots, and the
diameter increased with time. This demonstrated that the corrosion rate was
substantially controlled by charge transfer process, and it decreased with time.
In combination with the SEM results, the diameter increase in the Nyquist plot
was considered to be caused by the gradual formation of a dense corrosion
product film (Ref 36). In
SRB-containing medium, diameters of impedance loops decreased in the exponential
growth phase and increased slightly during the death and residual phases,
implying that corrosion of 907 steel was accelerated during the exponential
growth phase and inhibited in the other two phases.
×
The impedance spectra were further analyzed by fitting with proper
equivalent circuits shown in Fig. 9. In
the sterile medium, it was observed from SEM images that a uniform corrosion
product film covered 907 steel surface gradually, and consequently a two-time
constant model was adopted, which consisted of the corrosion product layer and
the electrical double layer (Ref 37). In SRB-containing medium, a three-constant time model was
selected based on the contribution of each phenomenon, such as the adsorption of
biofilm, the formation of corrosion product film, and the presence of electrical
double layer (Ref 16).
×
In these electrical analog circuits, Q, constant phase element (CPE), was applied instead of
capacitance due to the dispersion effects from heterogeneous surfaces, and it is
given by:
where Y0 is
a parameter related to capacitance, ω is
angular frequency, j is the imaginary number,
and n is an exponential term associated with
the roughness of electrode surface (Ref 38). Qbf, Qpf, and Qdl are CPEs of biofilm, corrosion
product film, and electrical double layer, respectively. Rs, Rbf, Rpf, and Rct correspond to the resistance of
electrolyte solution, biofilm, corrosion product film, and charge transfer,
respectively.
According to Stern–Geary equation, Rct is inversely proportional to the
corrosion rate, and its variation with time in different media is shown in
Fig. 10. Rct increased with time in the sterile
medium, which was attributed to the gradual formation of protective corrosion
product film that reduced the corrosion rate of 907 steel. The value of
Rct in
SRB-containing medium was larger than that in sterile medium on the first day of
exposure, which might be ascribed to the protection from EPS (Ref 39). Rct decreased sharply from day 1 to day
3, when SRB cells were in exponential growth phase and their quantity increased
dramatically, and it was believed that the high concentration of corrosive
metabolites (sulfide and organic acids) was responsible for the increased
corrosion rate. After the slight change from day 3 to day 7, Rct increased when the
residual phase came, which could be ascribed to the low metabolic activity of
SRB and the increase in the thickness of biofilm and corrosion product layer
(Ref 40). EIS results confirmed the
important role of SRB in the corrosion of 907 steel again, and the influence was
metabolic activity-dependent.
×
Current Distribution of WBE
Corrosion morphology revealed in Fig. 4 demonstrated localized corrosion induced by SRB, and the
WBE technique was further employed to give deeper comprehension of the localized
corrosion process. Figure 11 and
12 depicts the temporal evolution
of current distribution maps of WBE in sterile and SRB-containing media,
respectively. In the sterile medium, the maximum current density (imax) was
9.222 μA cm−2 after 1 day of immersion, and it
decreased to 3.755 μA cm−2 at the time of day 3.
Subsequently, the values of imax were smaller than
1.000 μA cm−2, and decreased gradually. When the
fresh 907 steel WBE was introduced into the electrolyte, it was susceptible to
corrosion attack since it was naked without any protection, resulting in a high
imax. Corrosion
products generated and accumulated with time on the electrode surface, retarding
the corrosion process, and lower imax was expected. Furthermore, the
distribution of anodic and cathodic sites changed with time. At the time of
day 1, anodes concentrated on the area with the corners of (2, 9), (6, 9), (6,
7), and (1, 6), and these sites behaved as cathodes at day 3 with the new
typical anodes at locations of (11, 10), (11, 8), and (1, 1). The initial anodic
sites might be due to their lower activation energy from material feature and
polishing treatment, and their polarity reversal was closely related to the
accumulation of corrosion products. After day 5, sporadic cathodic sites among
large anodic area turned to anodes gradually [such as sites of (8, 4) and (8,
8)], and cathodes concentrated on limited sites, demonstrating the development
of stable galvanic corrosion.
×
×
Different from that in sterile medium, imax was just
0.9234 μA cm−2 at the first day, and increased to
1.378 μA cm−2 at the time of day 3. Subsequently,
it stabilized at ca. 0.7 μA cm−2 during 5-9 days, and
decreased to ca. 0.6 μA cm−2 at the end of the test.
This evolution trend was also positively correlated with the growth curve of
SRB. Similar to the case without SRB, the distribution pattern of anodic and
cathodic sites changed greatly before day 3, and then stabilized. The initial
anodic current peaks located at the position of (10, 1) and (2, 1) vanished
after 3 days of exposure, and new peaks with the position of (8, 5) and (5, 7)
appeared on the fifth day in the death period, which could still be observed in
the residual period. This demonstrated that the electrochemically active sites
turned up at the beginning were not stable, and some stable sites formed
gradually with the immersion time extended. The heterogeneous biofilm composed
of SRB bacterial cells and their metabolites caused local gradient differences
and the enlargement of active sites (Ref 41), resulting in the localized corrosion of 907
steel.
To clarify the relationship between localized corrosion of 907
steel and metabolic activity of SRB, the variations of the ratio between
cathodic and anodic areas (r) as a function
of immersion time are presented in Fig. 13. Different from the case in sterile medium, where
r decreased in the first 7 days and then
kept stable, r in SRB-containing medium was
evidently related to SRB growth as it increased in the exponential growth
period, decreased in the death period, and maintained stable in the residual
period. Besides, r in SRB-containing medium
was much higher than that in sterile medium from the third day, suggesting that
there was a larger cathodic area and a smaller anodic area on the current
distribution map of 907 steel, which benefited the development of localized
corrosion. According to the classical cathodic depolarization theory (Ref
3), hydrogen evolution reaction
is promoted by SRB via the utilization of atomic hydrogen, and the efficiency of
cathodic depolarization highly depends on the activity of SRB. During the
exponential phase, cathodic hydrogen was consumed rapidly owing to the vigorous
growth and high metabolic activity, thereby promoting cathodic reaction and
leading to the appearance of a large cathodic area in the current distribution
map. In death and residual phases, the metabolic activity of SRB toward cathodic
hydrogen utilization was reduced, and accordingly, the cathodic depolarization
was weakened. These results are in good agreement with those from SEM, and the
localized corrosion of 907 steel induced by SRB is confirmed.
×
Conclusions
In summary, the influence of sulfate-reducing bacteria on corrosion
process of 907 steel was investigated in the present work. SRB could adhere on 907
steel surface forming a biofilm intertwined with EPS, resulting in the variations in
the chemical composition of corrosion products, the corrosion rate, and corrosion
type. Ferrous sulfide was generated as an important corrosion product due to the
metabolic activity of SRB. The introduction of SRB led to the enhanced corrosion of
907 steel, and the corrosion rate was closely related to the metabolic activity of
SRB. In a growth cycle, the corrosion rate increased, stabilized, and decreased in
the exponential growth, death, and residual periods, respectively. Localized
corrosion was induced by SRB, and its development process was tracked by the WBE
technology. Localized corrosion was facilitated via the larger ratio between
cathodic areas and anodic areas in the exponential growth phase, and gradual
formation of stable anodic sites in death and residual phases.
Acknowledgments
This work was supported by National Key Research and Development Program of
China (No. 2016YFB0300604), the National Natural Science Foundation of China
(41806087 and 51771180), Key Research and Development Program of Shandong Province
(No. 2018GGX104021), and AoShan Talents Cultivation Program supported by Qingdao
National Laboratory for Marine Science and Technology (2017ASTCP-ES02).
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