1. Introduction
Increasing population and industrial development cause a rapid increase in the demand of concrete. Concrete production requires massive amounts of fresh water that contributes significantly to water scarcity [1,2,3]. Concretes also use huge amounts of river sand that negatively impacts the river ecosystem, navigation and flood control [4]. In order to circumvent these problems, the use of seawater and sea sand concrete (SWSSC) is an attractive alternative. SWSSC is a recent type of concrete that can be improved further by use of alkali-activated slag as binding material. The mechanical properties of SWSSC are reported to be similar to those of the conventional Portland cement concrete [5,6,7]. The Japan Concrete Institute reported that the strength of the slag-containing concrete produced with seawater tends be higher as compared to the concrete produced using tap water [8]. Furthermore, the alkali-silica reaction has a detrimental effect on integrity of ordinary Portland cement concrete [9,10], whereas the geo-polymer concrete or the high-performance concrete that utilizes industrial waste materials such as fly ash or slag, instead of cement, is designed to reduce effect of the alkali-silica reaction.
Generally, mild steel rebars are employed as reinforcements to the concrete for high tensile strength and ductility; however, austenitic stainless steels have also been used because of their greater corrosion resistance. Steel bars develop a protective passive layer in the highly alkaline environment of concrete (pH > 10) [11]. However, this layer can be disrupted by chloride and other deleterious ions that diffuse from the marine or industrial environment through the concrete matrix on to the steel reinforcement surface, resulting in rapid corrosion of the bars. It is common to find the voluminous products of such rapid corrosion causing cracks and spallation of concrete (called “concrete cancer”), thereby seriously jeopardizing the durability of concrete structures. Therefore, the premature failure of reinforced concrete structure due to the corrosion of steel reinforcement is regarded as a critical durability problem that is a concern even for the normal reinforced concrete structures [12,13]. Such deterioration of steel reinforced concrete results in high repair and maintenance costs [14]. With the very-high chloride content of seawater, it is obvious that the corrosion rate of the traditional reinforcement of mild steel will be unacceptably high in SWSSC. Consequently, reinforcement of steels with much superior resistance to chloride-assisted corrosion, such as stainless steels (SS) may be required as replacement for mild steel. Stainless steel (SS) possesses superior corrosion resistance due to the presence of a very thin, robust, self-healing, passivating and protective surface layer of chromium oxide.
Cramer et al. [15] reported that the replacement of mild steel reinforcements with SS decreases maintenance costs by >50% with the projected service lives of normal concrete exceeding far greater than 100 years. Austenitic SS, AISI316, is among the most commonly used SS alloys where good corrosion resistance is required. SS 316 contains 16–18% chromium, 8–10% nickel and 2% molybdenum. Molybdenum is added for improving pitting corrosion resistance in chloride environment (such as seawater and deicing salts) [15]. However, too high chloride concentrations can disrupt the chromium oxide protective layer of SS, compromising their corrosion resistance and resulting in localized corrosion such as pitting [16,17].
Even though SS possesses significantly superior corrosion resistance compared with mild steel, they are susceptible to stress corrosion cracking (SCC), i.e., cracking of metals and alloys due to the synergistic action of corrosion and tensile stress [16]. SCC can result in a sudden, catastrophic and brittle form of fracture that eventuates because a crack initiates and sub-critically propagates, and a premature failure of components can consequently occur. Because SCC may occur at stresses below yield strength, it is among the most dangerous forms of corrosion-assisted fracture. Sometimes, residual stresses from fabrication or environments with small concentrations of harmful components may be sufficient to cause unexpected SCC [18,19]. Since pitting is among the common initiators of SCC [18], the ability of chloride in enhancing pitting susceptibility of SS becomes an obvious concern in using SS as reinforcement for SWSSC. Another application of the combination of SWSSC and SS is in the hybrid construction with SWSSC filled SS tubes [20].
There is already a range of studies focusing on the role of key variables in determining the susceptibility of SS to SCC. For example, Raman et al. [21] found pitting to be one of the common SCC-initiators, where the localized crack-tip dissolution facilitated crack propagation which is consistent with other published literature (e.g., [22,23]). A suitable synergy of mechanical loading and environmental condition is required for SCC cracks to propagate [24]. For example, when the passive film is less stable in high chloride environment, straining of metal at too high a rate may not allow enough time for effective passivation. In terms of alkalinity of environment, Truman [25] concluded that generally solutions of high alkalinity were less likely to give rise to stress corrosion cracking. However, a suitable synergy of the role of pH in enabling passivation and the role of straining in disruption of the passive film is required for SCC cracks to propagate, as demonstrated by Raman [24].
As described earlier, there is great interest in seawater sea sand concrete (SWSSC), including in hybrid construction. In such applications, stainless steels (SS) are potential material for reinforcing bars or tubes. Thus, this paper investigates stress corrosion cracking of AISI 316 SS in different environment relevant to SWSSC, with and without silicate, by slow strain rate testing (SSRT). For comparison, the SSRT tests were carried out in presence of the simulated solutions of seawater and normal concrete (with and without silicate). Though SCC of austenitic SS in chloride and caustic solutions has been investigated considerably (e.g., [21,22,23,24,25]), influence of silicate, a constituent of concrete, on SCC has not been investigated earlier. To the best of authors’ knowledge, this is the first report on deleterious role of silica in causing SCC to SS in concrete environment. This study investigates the role of a typical silicate addition to simulated concrete solutions in stress corrosion cracking of austenitic stainless-steel bars.
2. Experimental Procedure
The test samples were machined from the round bars of AISI 316 stainless steel (SS) which are procured from George Archer metals, Australia. The chemical composition of SS is (wt%) is: C (0.027), Mn (1.800), Si (0.360), S (0.026), P (0.038), Cr (16.800), Ni (10.060), Cu (0.450), Mo (2.030), Co (0.190) and N (0.075). The tensile strength of the steel was 660 MPa. The uniaxial cylindrical tensile specimen had an outer diameter (OD) 8.0 ± 0.2 mm, with a gauge section of 3.0 ± 0.2 mm OD and 20.0 ± 0.2 mm length. Figure 1 presents a schematic diagram of the tensile specimens used in the present study. To determine the susceptibility to stress corrosion cracking in the simulated solutions of seawater, normal concrete, and seawater sea sand normal concrete, the slow strain rate testing (SSRT) was employed. To achieve different constant crosshead speeds (i.e., different strain rates), the SSRT rig is equipped with a controlled variable speed motor. The speed can be varied from 10% to 100% of the full motor speed that corresponds to various strain rates in the range of 10−7 s−1. SSRT rigs were constructed locally at Monash University, and the variable speed motors for these rigs were procured from Baldor Electric company (Fort Smith, AR, USA).
Prior to loading the SSRT sample on to the SSRT rig, the gauge section was ground in the longitudinal direction progressively to a 2500 grit finish, rinsed with acetone and air dried. A layer of Teflon tape was used to cover all of the specimen surface except the gauge section that is exposed to the test solution within the corrosion cell of the rig. A clean SS sample was mounted onto the SSRT rig and the test solution was circulated at a constant temperature. The temperature-controlled water bath was used to maintain the temperature of the test solution at the ambient temperature (i.e., 25 °C) or 60 °C; the latter was selected to represent an extremely harsh condition. To examine the reproducibility, SSRT tests under each condition were duplicated.
Table 1 shows the chemical compositions and pH of the simulated solutions of normal concrete, with and without silicate addition (NC and NC_Sil) and seawater sea sand normal concrete, with and without silicate addition (SWSSNC and SWSSNC_Sil). As a reference 3.5% NaCl solution was used to simulate the seawater (SW).
SSRT tests were continued until fracture of specimens. Fracture surface of the failed specimens were cleaned using an inhibited acidic solution (hydrochloric acid and hexamethylenetetramine) and examined using a scanning electron microscope (SEM, Hitachi, Tokyo, Japan), for characterization of the fracture mode and identification of stress corrosion cracking. 3. Results and Discussion
Figure 2a presents the stress vs. time curves of the SSRT specimens tested at the strain rate of 3.7 × 10−7 s−1 at 25 and 60 °C in the simulated SW solution. Time to failure (tf = 296 h) at 60 °C was significantly shorter compared to that at 25 °C (374 h). The trend in the stress vs. elongation plots in Figure 2b is consistent with that seen in Figure 2a, i.e., the specimens tested at 25 °C displayed both the elongation-to-failure (Ԑf = 49.87%) and the ultimate tensile strength (UTS = 663 MPa) to be correspondingly higher than those of the specimens tested at 60 °C (Ԑf = 39.41% and UTS = 560 MPa).
It is necessary to ascertain whether SCC contributed to the shorter tf, and lower Ԑf and UTS at 60 °C, or these were simply just due the effect of higher temperature. Representative images of the fractographic features (Figure 3) suggest ductile dimples over almost the entire fracture surface of samples tested at 25 °C (Figure 3a), confirming absence of SCC, whereas the fracture surface of samples tested at 60 °C has a few locations with features of SCC (Figure 3b).
Figure 4a,b compare the stress vs. time and the stress vs. elongation plots respectively for AISI 316 stainless steel samples exposed to SW, NC and SWSSNC solutions at 60 °C. The tf, Ԑf and UTS in NC and SWSSNC are greater than the corresponding data for SW, which may be attributed to the high alkalinity (pH 13.4) of NC and SWSSC that facilitates the development of robust passive film [31,32], resulting in lesser corrosion-assisted loss of the sample cross-section. The corresponding similarities of the tf and Ԑf data for NC and SWSSC would suggest the passivating effect of high alkalinity in SWSSC (that is same as that in NC, i.e., pH 13.4) predominates the reported deleterious effect of high chloride content of SWSSC (35 g/l, i.e., same as seawater). As a result, both the environments seem to provide similar degrees of the lesser corrosion-assisted loss of the sample cross-section, and hence, corresponding similarities of the tf and Ԑf. In contrast, SW that has no alkali content (pH 7.5) will have the well-known influence in disrupting the passive layer of stainless steel [33,34,35], accelerating corrosion and loss of cross-section of SSRT samples, and hence, much lower tf and Ԑf in SW (Figure 4a,b).
Again, SEM fractography was carried out to ascertain whether SCC contributed to the fracture of specimens in NC and SWSSNC at 60 °C. Representative fractographic features (Figure 5) suggest only ductile dimples over the fracture surface, confirming absence of SCC in SWSSNC and NC at 60 °C.
One of the main degradation processes of the concrete structures is the alkali silica reaction (ASR) [36,37]. ASR occurs due to chemical reactions between hydroxyl ions in the pore water within the concrete matrix and certain forms of silica [9,37,38]. This reaction has a detrimental effect on ordinary Portland cement concrete which further deteriorates the integrity of the structure [9]. It causes cracking and collapse of concrete structures, including dams, bridges and pavements.
There is little reported on the effect of silicate in NC and SWSSC on SCC of steels. Figure 6a,b present SSRT results of 316 stainless steel in the simulated solutions of NC and SWSSNC with silicate (i.e., NC_Sil and SWSSNC_Sil respectively, as described in Table 1). The presence of silicate in NC and SWSSNC causes considerable decreases in tf, Ԑf and UTS in both NC_Sil and SWSSNC_Sil when compared to NC and SWSSNC (Table 2). For instance, the presence of silicate decreased the tf of 316 stainless steel samples by 19 and 47 h in the simulated solutions of NC_Sil and SWSSNC_Sil respectively (Figure 6a). Table 2 shows scatters in tf, Ԑf and UTS data of 316 stainless steel in the simulated solutions of NC, SWSSNC, NC_Sil and SWSSNC_Sil.
Tang et al. [39] studied the corrosion behavior of steel in simulated concrete pore solutions in the presence of calcium silicate hydrate (C–S–H). They found that the addition of silicate to the simulated concrete solution (pH 12.5) decreased passivation characteristics and increased the pitting corrosion sensitivity. The porous nature of C-S-H with high specific surface area enable it to adsorb the chloride ions effectively [39]. The accumulation of calcium ions near the interface can effectively attract chlorides and make them tightly bonded in spite of the electrostatic repulsion from the oxygen of surface silicate chains. Thus, the accumulation of calcium ions near the surface can effectively attract chloride ions [40].
SEM fractogarphy was carried out to find whether the shorter tf, and lower Ԑf and UTS at 60 °C in NC_Sil and SWSSNC_Sil could be attributed to SCC. The representative fractograph of the failed samples (Figure 7) suggests transgranular SCC over a considerable fraction of the fracture surface, whereas the rest of the fracture surface had ductile dimples. This observation suggests the deleterious role of silicate content in causing SCC.
Role of silica in deterioration of concrete due to alkali-silica reaction (ASR) is well-documented. However, there is little reported on role of the silica content of concrete in stress corrosion cracking (SCC) of steel rebar. As demonstrated in Figure 6a,b and Figure 7, silica addition to simulated solutions of normal and seawater and sea sand concretes causes stress corrosion cracking to 316 stainless steel. This finding suggests additional advantage of silica-lean concretes (such as the geo-polymer concrete or the high-performance concrete that utilizes industrial waste materials such as fly ash or slag).
This study investigated the cylindrical samples of austenitic stainless steel. In actual practice, SS bars may be welded. It is well known that welding may introduce residual stresses as well as undesirable changes in the steel such as sensitization in heat affected zone, both of which can facilitate SCC [41]. These aspects are a matter of further study.
4. Conclusions Use of seawater sea sand concrete (SWSSC) in place of normal concrete (NC) has great commercial and social implications. However, SWSSC may require stainless steel reinforcement (instead of mild steel used in NC). Stress corrosion cracking (SCC) of AISI 316 stainless steel (SS) was investigated at 25 and 60 °C by slow strain rate testing (SSRT) at 3.7 × 10−7 s−1, in simulated SWSSC and NC environments, with and without addition of silica (i.e., a constituent of concrete). SCC of SS was also investigated in simulated seawater (SW), for comparison. Following conclusions were drawn:
(a) SS showed no SCC at 25 °C in any of the test solutions;
(b) At 60 °C, some indications of SCC were seen in SW, but no SCC in SWSSC or NC;
(c) Highly passivating alkaline condition accounts for the absence of SCC in SWSSC and NC at 60 °C. The absence of SCC in SWSSC also suggests ineffectiveness of chloride content of SWSSC in causing SCC;
(d) The addition of silicate to SWSSC or NC caused transgranular SCC to SS at 60 °C, which may be the first finding of the role of silica in causing SCC to SS in concrete environment.
Figure 2.(a) Stress vs. time, and (b) stress vs. elongation plots of AISI 316 stainless steel alloy at strain rate of 3.7 × 10-7 s-1 in the simulated SW solution at room temperature (25 °C) and 60 °C.
Figure 3. SEM fractography of 316 stainless steel samples tested in SW at: (a) 25 °C and (b) 60 °C. Arrows shows the features of SCC that were located in the areas adjacent to the sample edge.
Figure 4.(a) Stress vs. time, and (b) stress vs. elongation plots of AISI 316 stainless steel alloy at strain rate of 3.7 × 10-7 s-1 in the simulated solutions of SW, NC and SWSSNC at 60 °C.
Figure 5. SEM fractography of 316 stainless steel samples tested in (a) NC and (b) SWSSNC at 60 °C.
Figure 6.(a) Stress vs. time, and (b) stress vs. elongation plots of AISI 316 stainless steel alloy at strain rate of 3.7 × 10-7 s-1 in the simulated solutions of NC and SWSSNC without and with silicate at 60 °C.
Figure 7. SEM fractography of 316 stainless steel samples tested in SWSSNC_Sil solutions at 60 °C. Arrows shows the features of SCC that were located in the areas adjacent to the sample edge.
Simulated Solution Nomenclature | Constituents (g/L) | pH | ||||
---|---|---|---|---|---|---|
NaOH | KOH | Ca(OH)2 | NaCl | Na2SiO3 | ||
NC a | 2.4 | 19.6 | 2.0 | 13.4 | ||
SWSSNC b | 2.4 | 19.6 | 2.0 | 35 | 13.4 | |
NC_Sil | 2.4 | 19.6 | 2.0 | 3.0 | 13.4 | |
SWSSNC_Sil | 2.4 | 19.6 | 2.0 | 35 | 3.0 | 13.4 |
SW | 35 | 7.5 |
a Simulated normal concrete (NC) pore solution is prepared according to [26]. b seawater sea sand normal concrete (SWSSNC) simulated pore solution is prepared according to [27,28,29,30].
Simulated Solution | Time to Failure (tf, h) | Elongation to Failure (Ԑf, %) | Ultimate Tensile Strength (UTS, MPa) |
---|---|---|---|
NC | 356 ± 6.8 | 47.4 ± 2.0 | 652 ± 6.6 |
SWSSNC | 356 ± 2.4 | 47.4 ± 0.3 | 606 ± 1.9 |
NC_Sil | 337 ± 5.2 | 44.9 ± 1.1 | 598 ± 3.9 |
SWSSNC_Sil | 309 ± 6.5 | 41.2 ± 1.8 | 596 ± 6.0 |
Author Contributions
R.K.S.R., conceptualization and planning of the work, supervision, funding and writing the manuscript; X.Y., conceptualization and planning of the work, experimental work, data analyses and writing the manuscript; S.A.-S., conceptualization and planning of the work, experimental work, data analyses, supervision and writing the manuscript; I.K., experimental work and data analyses; X.-L.Z., supervision, funding for the work and general technical discussions. All authors have read and agreed to the published version of the manuscript.
Funding
This research was funded by Australian Research Council (ARC) through an ARC Discovery Project Grant (DP160100739).
Institutional Review Board Statement
Not applicable.
Informed Consent Statement
Not applicable.
Data Availability Statement
Data is contained within the article.
Acknowledgments
The authors wish to acknowledge the financial support provided by the Australian Research Council (ARC) through an ARC Discovery Project Grant (DP160100739).
Conflicts of Interest
The authors declare no conflict of interest.
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Xiang Yu
1,
Saad Al-Saadi
2,
Isha Kohli
2,
Xiao-Ling Zhao
3 and
R. K. Singh Raman
1,2,*
1Department of Chemical Engineering, Monash University, Clayton, VIC 3800, Australia
2Department of Mechanical and Aerospace Engineering, Monash University, Clayton, VIC 3800, Australia
3School of Civil and Environmental Engineering, University of New South Wales, Sydney, NSW 2052, Australia
*Author to whom correspondence should be addressed.
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Abstract
Seawater and sea sand concrete (SWSSC) is a highly attractive alternative to normal concrete (NC) that requires huge amounts of fresh water and river sand. However, reinforcements of stainless steel (instead of mild steel that is used in NC) may be required for SWSSC. This article reports investigation of stress corrosion cracking (SCC) of AISI 316 stainless steel (SS) in simulated SWSSC and NC environments, with and without addition of silica to SWSSC and NC, employing slow strain rate testing (SSRT) at 25 and 60 °C. For the purpose of comparison, SCC of SS was also investigated in simulated seawater (SW) solution. SS showed no SCC at 25 °C in any of the test solutions. Indications of SCC were seen in SW at 60 °C, but no features of SCC in SWSSC and NC at 60 °C, as suggested by scanning electron microscopy (SEM) fractographs. While the absence of SCC in SWSSC and NC is attributed to the highly passivating alkaline condition, its absence in SWSSC also indicates the role of alkalinity to predominate the deleterious role of chloride content of SWSSC. However, the addition of silicate to SWSSC or NC triggers transgranular SCC to SS at 60 °C, as evidenced by the fractography.
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