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Article

Enhancing Corrosion Resistance of High-Carbon Steel by Formation of Surface Layers Using Wastes as Input

School of Materials Science and Engineering, Centre for Sustainable Materials Research and Technology (SMaRT Centre), University of New South Wales, Sydney, NSW 2052, Australia
*
Authors to whom correspondence should be addressed.
Metals 2019, 9(8), 902; https://doi.org/10.3390/met9080902
Submission received: 30 July 2019 / Revised: 11 August 2019 / Accepted: 14 August 2019 / Published: 16 August 2019

Abstract

:
Series of super-hard ceramic layers have been successfully developed on high carbon steels, with a significant improvement of corrosion resistance and hardness, without changing the original properties, which were derived from mixtures of slag (electric arc furnace), waste glass (bottles), and automotive shredder residue (ASR) plastics (polypropylene) via the single step surface modification technique. Microstructural analysis by laser scanning confocal microscopy (LSCM), crystallography analysis by X-ray diffraction (XRD), micro-level chemical analysis by scanning electron microscopy and energy dispersive spectroscopy (SEM and EDS), and depth profile surface analysis with three-dimensional chemical mapping by time-of-flight secondary ion mass spectrometry (TOF-SIMS), followed by electrochemical corrosion test by the Tafel method and hardness test—Vickers hardness measurement. Three areas have been classified, modified surface, interface, and main substrate areas as the synthesis of ceramic layers into surface of the steels that thermodynamically formed during the heat treatment process. Chemical composition analyses have revealed that generated layers consisting of chromium (Cr)- and magnesium (Mg)-based compound have shown an improved corrosion resistance to 52% and hardness to 70% without modifying the initial volume fraction of constituent phases–martensite and retained austenite. These findings have substantially highlighted to the potential use of waste-integrated inputs as raw materials for production in cost-effective way, concurrently decreasing the demand on new resource for coating, alleviating the disadvantageous impact to the environment from waste disposal in landfills.

1. Introduction

The high carbon steel (HCS) has been dominantly used for many mining and pharmaceutical applications due to its high reliability in strength, hardness, and abrasion resistance [1,2,3]. However, with a mediocre level of corrosion resistance, this grade of metal alloy is susceptible to corrosion, which can increase the cost of maintenance [3]. Corrosion protection for steel is fundamental for technological importance, due to the significant used in corrosive environment. Several methods have been developed to enhance the corrosion resistance of steels, for instance, adding alloying elements [4], applying protective coating [5], and surface alloying [6]. Although these methods are relatively effective in improving corrosion resistance, they have limitations. Adding alloying elements can affect other properties [4]. Furthermore, applying protective coating can attribute to thermodynamic restriction, causing chemical reaction between the bonding of layers to substrate, which can cause cracking [5]. On the other hand, using the surface alloying method requires uniform and homogenous energy dispersion to successfully achieve a desired microstructural modification [6]. Hence, implementing one of the methods can increase the use of new resource, time, and cost due to complex heat treatment, high precision machinery, and inflexibility of the process.
At the same time, there is significant unreached industry requirements for further surface modification to enhance the corrosion resistance and hardness without changing the original properties. To overcome the boundary, our research used a simple and economical solution via surface modification technology, which implemented single step and low temperature heat treatment and used waste-integrated inputs as the raw materials for production of surface layers. The objective of this study is to devise a more cost-effective process to enhance the corrosion resistance and hardness properties by producing super-hard ceramic surface with Cr- and Mg-based layers, “interface phase” or diffused layer between ceramic and without altering the bulk properties—substrate of steels (martensite and retained austenite phases).
Nonetheless, millions of tonnes of waste slag, glass, and automotive shredder residue (ASR) from different waste streams are annually discarded in the landfills [7,8], and it has been predicted to increase every year. Disposing these wastes not only will overlook the potential use of valuable elements, such as iron (Fe), silicon (Si), titanium (Ti), and carbon (C) [8,9], but also promote the harm environment to the surrounding area due to non-decomposable materials and potential of leaching. Using these wastes as the main source has the advantages of diminishing unnecessary issuance, energy, and new resource for coating production, and alleviating negative impacts to the environment. Moreover, the presence of chromium-based compound offers a superior coating characteristic, as it provides low coefficient friction and residual stress that are used for high wear and corrosion resistance applications [10,11]. Meanwhile, the magnesium-based compound has a high-level of thermal conductivity, hardness, wear, and corrosion resistance properties, and it is commonly used in various applications [12,13].
This study is important for designing the next applications of this grade of steel, as it consolidates two major issues and defines an effective solution by transforming the wastes into protective layers through single step heat treatment process. Not only enhancement in corrosion resistance and hardness without changing the bulk properties, but also incorporating with sustainability in materials processing to minimise the wastes ending in the landfills.

2. Materials and Methods

2.1. Material Preparation

Four high carbon steel (HCS) samples with chemical compositions of 0.99 C, 0.23 Si, and 0.98 Mn, 0.65 Cr (wt%) were adopted in this study. Waste-integrated inputs, such as slag, glass, ASR (ratio 1:1:1), with composition of slag—38.7 Fe2O3, 12.1 SiO2, 7.1 MnO, 29.8 CaO, 4.4 Al2O3, 7.0 MgO, 2.0 Cr2O3, balance (wt%), which were obtained from from Electric Arc Furnace and waste glass with 71.55 SiO2, 15.82 Na2O, 9.21 CaO, 3.95 MgO, balanced from bottles. These compositions have been characterised by X-ray Fluorescence (XRF) analysis. Polypropylene plastics from car bumper–ASR were used in this study and characterised by Fourier-Transform Infrared Spectroscopy (FTIR) analysis. Proposed innovative surface modification process at different heating temperature and dwelling time, sample labelling (as HCS-A, HCS-B, HCS-C, and HCS-D) in this study are presented in schematic diagram, as shown in Figure 1 with table. The 99.99% purity of Ar gas was pumped into closed chamber at 1 L/min. rate to simulate an inert condition. Four samples were successfully prepared, precisely cut to 15 mm × 15 mm × 3 mm dimension by Struers Accutom-50 (Struers, Rødovre, Denmark), grinded to 4000 grit by Struers Tegramin-30 (Struers, Rødovre, Denmark), polished up to 1 μm with diamond suspension by Struers Rotopol-22 (Struers, Rødovre, Denmark), ultrasonically cleaned by Powersonic 610 (Unisonics Australia, Brookvale, Australia), dried by Struers Drybox-2 (Struers, Rødovre, Denmark), and then etched by 2% Nital solution to reveal the phases.

2.2. Analytical Methods

Laser scanning confocal microscope (LSCM), Keyence VK-X250 (Keyence International, Mechelen, Belgium), and scanning electron microscope (SEM) Hitachi 3400N (Hitachi High Technologies America Inc., Schaumburg, IL, USA) were used for non-contact high-resolution imaging on the cross-sectional area of the samples, to analyse its surface topography and characteristic—main substrate, interface region, and modified surface or ceramic layer.
X-ray diffraction (XRD) analyses on the modified surface steels were carried out to observe the spectrum of the formation of surface layers and define its chemical composition, while using Empyrean (PANalytical) XRD (Malvern Panalytical Ltd., Malvern, UK), which was equipped with Co-Kα radiation to avoid strong effect from fluorescence of Cu radiation and achieve high resolution quantitative data. Used parameters, for example, current of 40 mA, voltage of 45 kV, recorded intensity from 2θ spectrum at angular range of 40° to 130°, and step size of 0.02.
Time-of-flight secondary ion mass spectrometry (TOF-SIMS) 5 spectrometer (IONTOF, Münster, Germany) was conducted for depth profile surface analysis with three-dimensional chemical maps on the region of interest–ceramic layer, by SurfaceLab software version 6.5 (IONTOF, Münster, Germany). Measurement strategy of Cs+ sputter beam at 1 keV that delivered 74.6 nA of target current over 300 × 300 μm2 area, with 45° incidence to the surface of sample. Dual beam mode was used with a pulsed 30 keV for Bi3+ in positive polarity, delivering 0.322 pA of target current over 100 × 100 μm2 area. The measurement of various elemental composition and concentration around a ceramic layer was carried out through energy dispersive spectrometer (EDS).
A Tafel polarisation technique was conducted by Versatile Multipotentiostat VSP-300 (EC-Lab©, Claix, France) that was equipped with EC-Lab v.11.10 software. Three different channels were connected to this instrument and a flat cell kit. Saturated calomel electrode (SCE) used for reference electrode, Pt electrode as counter electrode, and high carbon steel as working electrode. An electrolyte solution of 3.5 wt% NaCl was used for the experiments. The tested area was 1 cm2 in open circuit potential (OCP) for a four-hour experiment at room temperature, 24.0 ± 0.5 °C. The obtained Tafel curves were compiled in a range of −250 mV and 250 mV, sweeping rate of 0.3mV/s, and bandwidth of 8. Values of corrosion current density, icorr were defined through the cross path between anodic line (top section during discharging) and cathodic line (bottom section during charging) that vertically passed by corrosion potential, Ecorr, thus, the percentage of protective efficiency, ηPE was calculated.
Vickers hardness indentation method in 1 HV parameter was demonstrated from the top area (ceramic layer) and cross-sectional area (diffused layer and steel substrate) of the samples by Struers DuraScan-20 (Struers, Darmstadt, Germany), as per standard ASTM E140.

3. Results and Discussions

3.1. Microstructural Analysis

It was performed by LSCM on a cross-sectional area of high carbon steels at a different heat treatment condition in Figure 2. At different magnification and observation area (500 μm from edge of the steel substrate), HCS-A has constituent phases that consist of martensite and retained austenite in Figure 2a,a1. The XRD analysis of HCS-B sample has demonstrated the overall evidence of Cr- and Mg-based compound that presented in the ceramic layer, which required further in-depth investigations on its chemical composition while using SEM/EDS and TOF-SIMs analysis. Similar XRD patterns occurred on sample HCS-A and HCS-C samples, in which RA represents the retained austenite phase and M represents the martensite phase in crystallography patterns of 2θ.
On the HCS-B sample, the main substrate remained unmodified in Figure 2b, while uniform modified surface was formed up to 5 µm thickness with interface area on the edge surface as shown in Figure 2b1. Whereas, HCS-C exhibited a similar feature to original bulk characteristic with generated modified surface estimated to 18 µm in Figure 2c,c1 accordingly. Similarly, main substrate on HCS-D remained unchanged and modified surface accounted to 14 µm in Figure 2d,d1, correspondingly. Moreover, area between ceramic layer and main substrate, laid an interface region, where it has distinctive size, shape, and volume fraction of martensite and retained the austenite phases. Meaning that it could simply perform different behaviour on corrosion resistance and hardness properties on the outer surface of steel.
With relatively smaller grain size of both phases on HCS-B and HCS-D on interface region, it has higher potential risk of corrosion attack than HCS-C. This aspect was due to higher boundary-to-boundary contact and the difference in potential energy between phases, thus, prone to boundary and pitting corrosion [14,15]. The other aspect was because of martensite has higher carbon (C) content than retained austenite that possessed higher iron (Fe) content, resulting martensitic phase acted as cathode, whereas the austenitic phase referred as anode, hence preferential attack on retained austenite [14,15]. As results, bulk properties remained unmodified with layers being formed in three waste-treated samples through the reduction process of the wastes [16] into substrate of the steel.

3.2. Synthesis of Ceramic Layer into Steel Substrate

This occurred during heat treatment process that led to the degradation of organic materials and the formation of C-saturated gas from mixture of the wastes. The C-C bond in organic materials started to disintegrate and reaction between C and O2 in Cr2O3 and MgO to produce CO and CO2. The gases have been generated in the reduction process in the system and the appliance of various wastes instead of dependency on new resources (for example transforming coal to coke to produce C-source) and adopting single step with low temperature process, has led to a more environmentally friendly low-cost steel that was incorporated with less energy usage, including production time, thus the cost-effectiveness can be successfully developed. In this quick process, the different surface layer that has been achieved can dramatically improve the corrosion resistance and hardness properties of HCS. Two phenomena occurred on the surface of steel: firstly, the formation of metallic phase, as the presence of N2 in ASR plastics [8,9] will cause reduction reaction of Cr2O3 to CrN, including the formation of CrN from existing Cr element in steel and MgO to Mg3N2 and TiO2 to TiN. Secondly, the formation of oxide phases such as SiO2 and CaO. Moreover, high carbon steel acted as catalyse and Ar represented the carrier gas for all reactions.
Chromium nitride. As Cr and Fe have excellent chemical bond, as well as low wettability angle between these elements, existing Cr in steel and low quantity Cr in slag were simply bonded on the steel substrate during exothermic reaction [17]. This enables the diffusion and production of CrN on surface of the steel, as presented in equations [10,11], as below.
2Cr + N2 → 2CrN
Cr2O3 + 3C+ N2 → 2CrN + 3CO
Cr2O3 + 3CH4 + N2 → 2CrN + 3CO + 6H2
Magnesium nitride. The Slag and glass contain relatively large amount of Mg element in which, at 900 °C and above, is in the liquid phase. The Mg has a good chemical bond with Fe, and this enables the formation of Mg3N2 on the steel surface possible [18], equations [12,13], as shown.
3MgO + 3C + N2 → Mg3N2 + 3CO
3MgO + 3CH4 + N2 → Mg3N2 + 3CO + 6H2
The formation of other metallic phases, such as TiN from derived TiO2 in colour pigment of ASR for ultraviolet stabiliser, was produced during nitridation process [8,9]. Recent research has shown that the presence of H2 in the system will increase the reduction rate of metallic phases and iron acted as a catalyst for the formation of various ceramic compositions. With smaller diameter of H2 atoms and highly reactive behaviour, especially with O2, thus, its presence accelerated the reduction rate of oxides [19]. Other compounds that are present in the ceramic layer are oxide phases, such as SiO2, which are highly concentrated in glass and ASR [20]. On the other hand, CaO was mainly found in slag and glass composition. Interestingly, this composite behaviour of metallic and ceramic phases have been synthetically formed during the heat treatment process. A different gradient of elements on ceramic surface to substrate of the steel was presented in SEM and EDS analysis, as demonstrated in Figure 3. EDS mapping of C, N, Fe, Cr, Mg, Si, Ca, Ti, O, and Mn elements have clearly exhibited different thickness of chemical-bonded layer into steel substrate. Further analysis on its hardness has been conducted and explained.

3.3. SEM/EDS Analysis

It can be observed that Cr-based layer was consistently presented underneath the Mg-based layer, in which it can act as secondary protection after Mg-based layer has been removed by applied friction force. This is due to mainly presence of Cr in steel to synthetically form Cr-based layer near the surface of steel that through selective diffusion process—exothermic reaction [17]. The composite behaviour can offer different corrosion and hardness properties of steels. Moreover, HCS-B formed a uniform and the thinnest ceramic layer that consisted of highly concentrated CrN, Mg3N2 and low concentration of TiN bonded to the steel substrate, Figure 3a. As the temperature increased, the concentration of Ca was substantially reduced due to its melting point being exceeded. Furthermore, the cavities—C element presented as resin of the mounted sample occurred at higher heat treatment temperature on the ceramic layer of HCS-C and HCS-D, as the gases remained trapped during volatilisation and gasification processes from the wastes [21]. These cavities can decrease the abrasion resistance properties of steel, as it has higher potential to wear off than the uniform characteristic of the ceramic layer on HCS-A. Despite these cavities, the thickness of super-hard ceramic was the thickest on HCS-C, as shown in Figure 3b, than all of the samples, including HCS-D in Figure 3c, in which could promote the higher-level of protection from corrosion degradation and hardness properties. However, further investigation on electrochemical and hardness properties are necessary to incorporate the microstructural analysis with chemical property results.

3.4. XPS Analysis

Sample HCS-D has been chosen for the further investigation on two-dimensional mapping and three-dimensional chemical composition via TOF-SIMS analysis by an ion sputtering method to acquire a desire depth profile by removing the micron size outer layers. This sample was selected for balance between better thickness of ceramic layer than HCS-B and less porous than HCS-C. From this Figure 4, the global TOF-SIMS positive ions depth profiles of C+, N+, Fe+, Cr+, Mg+, Si+, Ca+, and Ti+ ions that were obtained for the ceramic layer. The results have suggested, in a good agreement with SEM/EDS chemical analysis results as well as XRD analysis, a consistent elemental composition of a strong presence on Cr, Mg, and N-rich compounds that mainly formed in the ceramic layer.
From this graph, as the sputter time increased, the Fe+, Cr+, and Si+ signals were gradually increased with exposure to the main substrate steel that caused this phenomenon. Whereas, the trend of ions of Ca+, N+, and Mg+ were slightly decreased as the ion beam penetrated deep into the ceramic layer and near the main substrate of steel. The selective diffusion occurred between the bonding of the ceramic layer that was derived from different waste, into steel substrate. This bonding was believed to be due to the shift balance from thermodynamic perspective between Fe+ ions that were produced from mainly slag that contained less C content to higher C content that already present in main substrate of the steel. Cr and Fe have excellent, as well as low, wettability and diffusivity; Cr oxide in slag that has been through reduction process in heat treatment and the presence of Cr in steel, bonded into steel substrate with iron, acted as catalyst during the exothermic reaction. This enables the diffusion and production of CrN on surface of the steel. Slag and glass contained a relatively high volume of Mg element, in which, at this heating temperature, it was in the liquid state. Similarly, Mg has good chemical bond with Fe, and this makes the formation of Mg3N2 on the steel surface possible, which is in good agreement with TOF-SIMS depth profile analysis.

3.5. Electrochemical Corrosion Test

Investigation of the electrochemical corrosion properties by Tafel method was conducted to analyse the effect of generated layers on corrosion rate, as shown in Figure 5. To define improvement in corrosion resistance, lower icorr value and more positive Ecorr value toward noble side were required. Protection efficiency, ηPE values were calculated against HCS-A by the standard equation [22]. As consequences, the corrosion protection efficiency contributed around 18.35%, 51.96% and 35.44% on HCS-B, HCS-C, and HCS-D, respectively. The protective efficiency values were obtained against the base-material (HCS-A) or before heat-treated using wastes. HCS-C possessed the highest corrosion resistance as it has the thickest coating, leading to its highest improvement. Additionally, this improvement has direct effect on the presence of CrN and Mg3N2 in the ceramic layer, as they tend to have corrosion resistance nature. While, HCS-B has lowest protection, since its six-hour dwelling time, followed by HCS-D heat-treated at higher temperature, which was caused by volatilisation and gasification from most wastes, hence increased the decomposition rate that led to direct effect on diffusion rate and reduction reaction of metallic and oxide phases into steel substrate.

3.6. Microhardness Test

Vickers hardness measurement was conducted on high carbon steels before and after the heat treatment process, as summarised in detail in Figure 6. The hardness of HCS-C was the highest, increased up to 1394 HV or 69.79% and 983 HV or 19.73% improvement on its super-hard ceramic layer from approximately 821 HV on HCS-A. This significant increase was associated with the effect of the presence of dominant Cr-based compound that was well-known as its interstitial compound, in which the N2 atoms occupying octahedral gaps in Cr lattice thus offered not only extremely high-level corrosion resistance, but also very hard nature property. Combination with Mg-based that commonly known as its nitrides of alkaline earth metals, normally used as hard coating, offered hardness property nature in this compound, aside from the temperature and dwelling time of heat treatment on the waste-integrated input.

4. Conclusions

The enhancement of corrosion resistance and hardness properties of high carbon steels have been successfully achieved by single step surface modification method while using waste-integrated (slag, glass and ASR) as source of inputs. At different heat treatment temperature, the ceramic layers have become a favourable outcome in an economical way of modified surface. Series of ceramic layers have been developed and its bulk properties remained unmodified through microstructural analysis by laser scanning confocal microscopy. XRD result has shown the strong presence of Cr- and Mg-based compound of generated ceramic layer. The effect of a different heat treatment parameter has a direct effect on the thickness of overall ceramic layer bonded on surface of high carbon steels. This generated a super-hard ceramic layer that mainly consisted of Cr- and Mg-based elements that has been proved through cross-sectioned SEM/EDS analysis and in-depth TOF-SIMS depth profile chemical analysis by sputtering ions. Electrochemical analysis by the Tafel method has showed significant improvement on corrosion resistance of nearly 52% and hardness to 70% than base-material. The results highlighted a very notable potential used of various wastes as valuable resource for production that promoted cost effectiveness, simultaneously minimising the needs of additional energy and time in the manufacturing process, dependency on new resource for alloying or coating, and the alleviating negative impact to the environment from waste disposal in the landfills.

Author Contributions

W.H. designed and performed experiments and data analysis. F.P. performed experiments and critically analysed the data. V.S. supervised the study and gave recommendations to revise manuscript. W.H. wrote the manuscript and all authors analysed data, discussed the results, read and approved the final manuscript.

Funding

This research was funded by Australian Government Research Training Program (RTP) and Australian Research Council’s Industrial Transformation Research Hub, grant number IH130200025 and The APC was funded by project IH130200025.

Acknowledgments

This research was supported under Australian Government Research Training Program (RTP) and Australian Research Council’s Industrial Transformation Research Hub funding scheme (project IH130200025). We gratefully acknowledge the technical support provided by Electron Microscope Unit at Mark Wainwright Analytical Centre, UNSW Sydney.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Schematic diagram of proposed surface modification process for formation of super-hard ceramic layer on high carbon steel (HCS) from waste-integrated inputs by single step heat treatment at different temperature and dwelling time.
Figure 1. Schematic diagram of proposed surface modification process for formation of super-hard ceramic layer on high carbon steel (HCS) from waste-integrated inputs by single step heat treatment at different temperature and dwelling time.
Metals 09 00902 g001
Figure 2. Laser scanning confocal microscopy (LSCM) images of cross-sectional area of main substrate on high carbon steels, which (a) HCS-A; (b) HCS-B; (c) HCS-C; and, (d) HCS-D with each interface and modified surface on (a1d1) respectively. The (e) X-ray diffraction (XRD) analysis on the generated surface layer on sample HCS-B that demonstrate the presence of complex Cr- and Mg-based compound on the ceramic layer. Where RA refers to retained austenite and M refers to martensite.
Figure 2. Laser scanning confocal microscopy (LSCM) images of cross-sectional area of main substrate on high carbon steels, which (a) HCS-A; (b) HCS-B; (c) HCS-C; and, (d) HCS-D with each interface and modified surface on (a1d1) respectively. The (e) X-ray diffraction (XRD) analysis on the generated surface layer on sample HCS-B that demonstrate the presence of complex Cr- and Mg-based compound on the ceramic layer. Where RA refers to retained austenite and M refers to martensite.
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Figure 3. Energy dispersive spectrometer (EDS) intensity maps for C, N, Fe, Cr, Mg, Si, Ca, Ti, O, and Mn at cross-sectional area of high carbon steels after heat treatment using waste-integrated inputs at different temperature (a) HCS-B, (b) HCS-C, and (c) HCS-D.
Figure 3. Energy dispersive spectrometer (EDS) intensity maps for C, N, Fe, Cr, Mg, Si, Ca, Ti, O, and Mn at cross-sectional area of high carbon steels after heat treatment using waste-integrated inputs at different temperature (a) HCS-B, (b) HCS-C, and (c) HCS-D.
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Figure 4. Time-of-flight secondary ion mass spectrometry (TOF-SIMS) (a) two-dimensional (2D) mapping and three-dimensional (3D) chemical analysis on the desire depth profile on near surface region of interest from ceramic layer to examine C+, N+, Fe+, Cr+, Mg+, Si+, Ca+, and Ti+ ion signals of the HCS-D sample. The summary of (b) intensity of each ions over sputter time graph.
Figure 4. Time-of-flight secondary ion mass spectrometry (TOF-SIMS) (a) two-dimensional (2D) mapping and three-dimensional (3D) chemical analysis on the desire depth profile on near surface region of interest from ceramic layer to examine C+, N+, Fe+, Cr+, Mg+, Si+, Ca+, and Ti+ ion signals of the HCS-D sample. The summary of (b) intensity of each ions over sputter time graph.
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Figure 5. Comparison of Tafel extrapolation curve of studied high carbon steel samples.
Figure 5. Comparison of Tafel extrapolation curve of studied high carbon steel samples.
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Figure 6. Summary of hardness values at in different tested area of high carbon steels.
Figure 6. Summary of hardness values at in different tested area of high carbon steels.
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MDPI and ACS Style

Handoko, W.; Pahlevani, F.; Sahajwalla, V. Enhancing Corrosion Resistance of High-Carbon Steel by Formation of Surface Layers Using Wastes as Input. Metals 2019, 9, 902. https://doi.org/10.3390/met9080902

AMA Style

Handoko W, Pahlevani F, Sahajwalla V. Enhancing Corrosion Resistance of High-Carbon Steel by Formation of Surface Layers Using Wastes as Input. Metals. 2019; 9(8):902. https://doi.org/10.3390/met9080902

Chicago/Turabian Style

Handoko, Wilson, Farshid Pahlevani, and Veena Sahajwalla. 2019. "Enhancing Corrosion Resistance of High-Carbon Steel by Formation of Surface Layers Using Wastes as Input" Metals 9, no. 8: 902. https://doi.org/10.3390/met9080902

APA Style

Handoko, W., Pahlevani, F., & Sahajwalla, V. (2019). Enhancing Corrosion Resistance of High-Carbon Steel by Formation of Surface Layers Using Wastes as Input. Metals, 9(8), 902. https://doi.org/10.3390/met9080902

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