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Environ Eng Res > Volume 23(2); 2018 > Article
Galai, Benqlilou, Touhami, Belhaj, Berrami, and El Kafssaoui: Comparative analysis for the corrosion susceptibility of copper alloys in sandy soil


Corrosion of copper alloys (copper, bronze and brass) in soil was evaluated at ambient temperature using various methods such as electrochemical impedance spectroscopy (EIS), polarization curves and Scanning Electron Microscopy (SEM) coupled with Energy Dispersive Spectroscopy microanalysis measurements. Three equivalent circuits were separately used to interpret the obtained impedance spectra. The EIS measurements indicated that the polarization resistance of all electrodes increases with increasing the immersion time. SEM showed a presence of three layers of corrosion products with various composition and morphology covering each electrode. In addition, it was found that at 20% of moisture content the Rp values and the current density of all electrodes in the studied soil give the following order: copper > bronze > brass. Good consistency between the data obtained from EIS and PP measurements was observed.

1. Introduction

Copper and its alloys have been used for more than 10,000 y and are widely used in various industrial fields thanks to their interesting properties. In particular, these properties are high electrical and thermal conductivities, good chemical weld-ability and especially, the good resistance to corrosion. In addition, the copper and brass are used in the sanitary industry to make drinking water pipes and plumbing devices.
Copper present an excellent resistance to corrosion in unpolluted air and drinking water. However, copper materials can undergo significant corrosion under various conditions, like the presence of sulphates, chlorides or nitrates. It is therefore important to find the right copper alloy by considering the environmental conditions to which it will be exposed [1].
The intensity of dezincification of brass is very closely related to the structure of the alloy which is controlled by composition. As might be expected the resistance to this dezincification increases with copper contained in brass, but this relationship is not linear. Many positive changes in performance take place when the structure changes from all-beta to(α+β) duplex and from duplex to all-alpha phase. The alloys that contain less than 15% Zn rarely undergo dezincification [2, 3].
Bronze like brass is a common structural material and was one of the first alloys developed by ancient metal workers. Bronze is a copper alloy containing tin, generally in the 1 to 10% range. The addition of tin increases the bronze hardness making it more resistant to wear when compared with pure copper metal [4].
Corrosion means a deterioration of a metal or properties which defines this metal due to an environmental reaction. The corrosion in soil is a strongly intricate phenomenon with a variety of factors involved like soil particle size, moisture content, degree of aeration, pH, redox potential, resistivity, soluble ionic species (salts) and microbiological activity. Many surveys of the degradation of metal used in plumbing devices that depend on the soil type reveal soil parameters such as soil texture, soil acidity, and the quantities of soluble salts like Cl and SO42− which foster the corrosion of metal objects [58].
In the present study, the Essaouira site was the location where a complaint was made about the corrosion of fitting brass (gate valves) which connects the PVC’s conduits. Indeed, because of this problem, thus a convention with The National Office of Electricity and the Drinking Water (ONEE) and our laboratory have been made to study the corrosion of gate valves in other sites in Morocco. In various studies [912] the authors were interested in steels pipeline corrosion in soil. But the ONEE company required to use the copper alloys as a gate valve. Therefore, our mission is to investigate the effect of soil on the corrosion behavior of three materials; copper, bronze and brass in sandy soil from Essaouira city of Morocco at ambient temperature (25 ± 2°C).

2. Materials and Methods

2.1. Soil Sample Preparation

A fraction of the soil was taken from 1 m deep under the ground at collected in a suburban area of Essaouira site in Morocco was dried at 105°C for 24 h and then left in the desiccator (DURAB, Germany). Soil sampling and analysis is performed following the procedures described elsewhere [13].
Table 1 gives the concentrations of the elements and the texture that have been analyzed in the original soil sample. So, from the texture, we can classify the sample as a sandy soil.
In addition, the electrochemical cell which was specifically designed for this study is represented in Fig. 1 respecting the literature [14].
Each soil sample was compacted manually in the electrochemical cell by applying a Proctor Compactor that consists of 3 kg soil which is dropped from a height of 150 mm. The atmosphere inside the cell was constantly renewed via a flow of reconstituted air (80% of N2 and 20% of O2) which circulated on the soil surface in the upper part of the cell.

2.1.1. Composition of metallic materials

The chemical composition of copper, bronze, and brass are presented in Table 2. Chemical composition analysis was performed by optical emission spectrometer (BRUKER, French).
The different material specimens encapsulated by an epoxy-resin were used as a working electrode with an exposed area of 0.78 cm2. Before each test, the sample was polished with abrasive paper up to 1,200 grit, rinsed with deionized water, degreased with ethanol (EMSURE, Reag. Ph Eur made in Germany) and finally dried in air.

2.2. Electrochemical Methods

2.2.1. Electrochemical impedance spectroscopy

Electrochemical impedance spectroscopy (EIS) measurements were performed using a transfer function analyzer (Volta Lab PGZ 100, Radiometer Analytical, French) frequency response analyzer in a frequency range of 100 kHz to 10 mHz with 10 points per decade with a small amplitude a.c. signal (10 mV). The EIS diagrams were done in the Nyquist representation. The results were then analyzed according to an equivalent electrical circuit using Bouckamp software [15].

2.2.2. Polarization tests

The counter electrode was a stainless steel plate with 9 cm2 of surface area whereas reference electrodes were copper-copper sulphate electrodes Cu/CuSO4 (ADCA SA, French) with (+0.316 V/SHE at 25°C) which were commonly used in the field. In the following sections of this article, all potentials are presented according to this reference electrode.
In addition, the working electrode was immersed in the soil during 21 d until a steady state open circuit potential (Eocp) was reached. The steady-state polarization curves were recorded potentiodynamically using a Volta Lab PGZ 100 and controlled by a personal computer. The cathodic polarization curve was recorded by polarization from (Eocp) to negative direction (−1,500 mV/Cu/CuCuSO4) under potentiodynamic conditions corresponding to 1 mVS−1 (scan rate). After this scan, the anodic polarization curve was recorded by polarization from (Eocp) to positive direction (1,200 mV/Cu/CuCuSO4) under the same conditions as said before. The corrosion kinetic parameters were evaluated again by means of non-linear least square method and by applying Eq. (1) using origin software. Nonetheless, for this calculation, the potential interval chosen was limited to ±0.100 V beside Ecorr, and a significant systematic divergence was sometimes noticed for both cathodic and anodic branches.
i=ia+ib=icorr×{exp [ba×(E-Ecorr)]-exp [bc×(E-Ecorr)]}
Where icorr is the corrosion current density and Tafel plots: ba (anodic) & bc (cathodic) which are attached to Tafel slopes β and expressed in logarithmic scale by the following equation:
β=ln (10)b=2.303b

2.3. Scanning Electron Microscopy (SEM)

Examination of all studied electrodes after exposure into the sandy soil after a hold time immersion of 130 d, was carried out using scanning electron microscopy (SEM; JOEL JSM-5500 made in Japan) before observation these specimens were rinsed thoroughly in a nonreactive solvent (alcohol) to prevent further corrosion.

3. Results and Discussion

3.1. EIS Measurements

The EIS measurements were carried out at corrosion potential. The Nyquist diagrams were registered for different electrodes in Essaouira soil and at different times from 1 to 21 d at 20% of moisture content as shown in Fig. 3 and Fig. 5.
Three equivalent circuits were obtained: the first is for the corrosion of brass in Essaouira soil (Fig. 2(a)) the second (Fig. 2(b)) is for the corrosion of copper whereas the last one is for the corrosion of bronze in the same soils (Fig. 2(c)).
In the case of brass, equivalent circuits consist of solution resistance Rs connected in series with two time constants R1[Q1(R2Q2)]. The Q symbol mean the possibility of a non-ideal capacitance (CPE, constant phase element) where n is the variable. The impedance of the CPE is given by the following equation [16]:
For n = 1, the Q element reduces to a capacitor with a capacitance C and, for n = 0, to a simple resistor. Firstly, the process (Rf, Qf) at higher frequencies in the soil parameter Qf represents the capacitive behaviour of the passive film formed at the surface, coupled with resistance due to ionic paths through oxide film Rf. Secondly, the process (Qct, Rct) is detected at low frequencies, Qct represents the capacitive behavior at the electrolyte/metal interface (i.e. the double layer) and Rct represents the corresponding charge transfer resistance.
In the case of bronze, the corresponding equivalent circuit for EIS tests was shown in Fig. 2(c) There are two time constants in the equivalent circuit diagram that describe the corrosion process of bronze in sandy soil, where Rs is the sandy soil resistance between working electrode and reference electrode, and QfRf represents the capacitance and resistance of the corrosion product film on the metal surface; RctQl corresponds to the charge transfer resistance and a constant phase element (CPE), and W represents the Warburg diffusion impedance whose value can be expressed as:
In the case of copper, the obtained impedances spectra exhibit three semicircles from high to low frequencies. So, two semicircles badly separated at high-frequency domain and the third one is at low-frequency domain. At high frequency (HF), the first semicircle may be attributed to the adsorbed specie, whereas the second one is the response of a combination of Rct and constant phase element (CPE). At low frequency (LF), the obtained loop is generally assigned to a slow transport process like diffusion [17, 18]. However, the Warburg impedance is introduced because it reflects the diffusion process of dissolved oxygen from the soil to the electrode surface and/or the diffusion process of soluble copper species in the reverse sense. In addition, the capacitive semicircle is commonly assigned to the double–layer capacitance (Cct) and charge transfer resistance (Rct). Deviations from a perfect circular shape (depression) are often related to the frequency dispersion of interfacial impedance arising from a lack of homogeneity of the electrode surface due to roughness or interfacial phenomena [19]. The proposed electrical circuit, as shown in Fig. 6, was used to describe the copper/electrolyte interface model. The employed circuit allowed for the identification of solution resistance (Rs), charge transfer resistance (Rct) and resistance associated with the layer of products formed (Rf). It is worthy of note that the double-layer capacitance (Cct) value was affected by imperfections of the surface, and this effect was simulated via a CPE [20, 21]. The Qct and n parameters are employed in case the surface heterogeneity may affect them, this heterogeneity can be a result of surface roughness, corrosion product adsorption, and porous layer formation. Therefore, the expression differs from the CPE impedance frequently used nowadays, where the impedance of parallel connection of the CPE and R will be expressed as [22]:
For the former, the capacitance has the unit of F (or F cm−2), whereas the later involves the remaining time dimension and CPE has the unit of F Sn–1 or (F Sn–1 cm−2). Wheren is the coefficient representing the frequency dispersion of capacitive time.
EIS data analysis is based mainly on the carrying out of equivalent circuits in order to model the metal/electrolyte (in our study copper alloy/soil) interface to represent the experimental diagrams, various equivalent circuits were applied using a Bouckamp software [15].
Table 3 represents the estimated electrochemical impedance parameters for all electrodes corrosion in the studied soil with 20% of moisture contents at different immersion times. The The data used for polarization resistance Rp of the studied systems are listed also in Table 3. Its value was calculated using the following equation:
It is noted that the Rp values of all brasses increase with the immersion time. The highest value of Rp recorded of various electrodes after 20 d of immersion can be attributed to the formation of a protective layer on the metallic surface which is related to the chemical composition of each electrode such as Cu, Zn and Sn. A long immersion of these alloys in the soil media raises the resistance of its barrier film and becomes stable after 21 d of immersion in Essaouira soil.
However, it can be observed that the Warburg impedance disappears in the case of brass. Only some large convex arcs are observed in the Nyquist plots, demonstrating that brass corrosion is controlled by the charge transfer process in this condition [23].
It is noticed from Table 3 that the values of both Rct and Rf increased with immersion time demonstrating that the protective film formed on copper and its alloys surface is composed of corrosion product. Furthermore, the values of Cf and Cct, which can be expressed below as Eq. (7) and (8) indicated in the study [23, 24] decrease with increasing immersion time.
Where S is the surface area of electrode exposed in the corrosive medium (soil), d is the thickness of electric double-layer, F is the Faraday’s constant. ɛ0 and ɛ are the permittivity of the air and the local dielectric constant, respectively. Therefore, the decrease of Cf can be interpreted with the formation of the protective film, which reduces the exposed electrode surface area at the corrosive medium.
In addition, according to the results of parameter data obtained, we end in the following classification for the all electrodes as follows:
In this soil, the electrolyte resistance (Rs) was found to increase with the immersion time. This increase can be related to the change in the composition of the soil which becomes less conductive due to the decrease in Cl and SO42− ions which are deposited on electrode surface to form corrosion products.

3.2. Potentiodynamic Polarization

Fig. 6 shows the polarization curves obtained on a large potential range (from 1,500 mV/Cu/CuSO4 to 1,200 mV/Cu/CuSO4) at the end of the 21 d of immersion for the three electrodes under investigation in the Essaouira soil at 20% of moisture content. Their corresponding parameters like potential of corrosion (Ecorr), anodic (βa) and cathodic (βc) Tafel slopes, and corrosion current density (icorr) of all studied systems were fitting by equation of Stern–Geary and registered in Table 4.
Fig. 7 shows the simulation results of the cathodic and anodic branches for different electrodes in sandy soil after an immersion of 21 d. In this simulation, the potential domain is in the vicinity of corrosion potential, Ecorr + -100 mV. The calculated data agrees with the experimental polarization data in Fig. 6.
It can be seen from Fig. 6 that besides the Ecorr (region (I)) the charge transfer and mass transport are both the factors which control kinetics are commonly assumed and thus the Tafel behavior of the curve is only “apparent”. In region (II), we can notice the appearance of a peak in all anodic part (peak current density (ipeak)). In this peak, the current density decreases due to the formation of a CuCl film [25]. In region (III), the potential increases again before stabilizing (passive region). This region is about 0.9 V from +0.3 V to +1.2 V over which the current density is constant. This plateau is attributed to the formation of protective oxide film on surfaces of samples [26].
In general, the corrosion of Cu alloys, in neutral chloride solutions, involves the cathodic reduction of oxygen:
In the anodic region, the dissolution of copper alloys in the medium containing the chloride ions, generates the following steps:
  • - Spontaneous dissolution of copper oxide Cu2O formation:

  • - When the surface is covered with Cu2O and ZnO, CuCl is then formed on the surface according to the reaction:

    This last CuCl can transform into CuCl2 according to the reaction: [2729]
    or dissolves with the formation of CuCl2 complex via: [2729]
The values of the current density of the three different electrodes were calculated at the same soil. Under the same conditions, copper is the most resistant electrode in this soil. The corrosion rate of the copper is less than 3 and 4 times in comparison with the bronze and brass respectively and we can follow this classification:
We can explain this classification as follows:
The brasses will be sensitive to dezincification process when the zinc components are higher than 15% [30]. In another study by Lucey [31], two mechanisms have been proposed for dezincification of brass:
  • - the first mechanism suggests that the Zn is leached out of the alloy.

  • - the second mechanism proposes that the entire alloy dissolves, but the Cu is redeposited on the surface.

Moreover, in this research, the bronze is more resistant compared with brass due to the chemical composition of bronze which contains a lower percentage of zinc 5%. The presence of tin in bronze with 5% improves resistance to corrosion due to the formation of Sn compounds that cover the surface and confer to the interface a blocking behavior.

3.3. Characterization of Corrosion Layers by SEM-EDS Analysis

The study of electrochemical behavior is not sufficient to explain the degradation process. Therefore, to have a very deep understanding of degradation process, we have to connect this process to the structure and composition of the corrosion product layer which is formed on surface alloys. SEM-EDS analysis was done on three electrodes. Fig. 8, 9 and 10 give the corresponding SEM images of bronze, brass and copper respectively under investigation after 130 d of immersion in sandy soil at 20% of moisture content. The data of EDS analysis of the corrosion product formed on the each electrode surface are presented in Table 5.
Observed differences between copper, bronze and the copper exposed in Essaouira soil at 20% of moisture content were evident not only from differences in visual appearance, measured corrosion rates and polarization resistance, but also from the analysis and characterization of corrosion products, illustrated after 130 d of immersion. The copper surface immersed in soil (Fig. 10) shows a large area free of corrosion products and the surface is intact as the polishing stripes remained perfectly visible on it even after exposure. The surface of bronze (Fig. 8) observed was uniform, compact and covered with a corrosion product. In other words, the film seems to be more compact and thicker on the surface. The observation of brass surface (Fig. 9) reveals peeling of the surface layer (cracked layers). Furthermore, it is noticed that the corroded surface shows many pits; consequently, this porous structure and the presence of the crevices in the corrosion layer produced the channels which let the diffusion of elements of corrosive medium (water, oxygen, salt ions and other corrosive media) through metal substrate [32].
The EDAX analysis was employed to determine the elemental composition of corrosion products formed on surface of the three samples after 130 d of immersion in sandy soil Essaouira. The results of this analysis are shown in Table 5. These data show that copper surface contains a large percentage of Cu with a lower percentage of oxygen which explains the presence of Cu oxides but with very little percentage. In the case of the bronze primary elements detected were Zn, Cu, O and Cl along with, Ca, C, Sn, Pb, etc. Main corrosion products are expected to be oxides and chlorides of Zn and Cu. The higher percentage of Sn on the surface of bronze indicates that Sn agglomerated at the corrosion product/metal interface and then formed a passive film which increases the resistance of bronze to generalized corrosion [33].
Concerning the brass, the EDAX shows that the corrosion product contains a large percentage of Cu and Zn with a high percentage of oxygen which explains the presence of Cu and Zn under oxides form. In addition, the presence of the Al, Ni, Mn and Fe (additional element in brass compositions) on the surface of corrosion product approves the surface degradation and consequently the corrosion rate becomes greater. Moreover, soil elements such as Fe, Si, Ca, S, Mg, C are detected in the corrosion product. The results that are obtained by EDAX and scanning electron microscopy are in agreements with those of the polarization and impedance measurements.

4. Conclusions

Comparative analysis for the corrosion susceptibility of copper, bronze, and brass in the soil of Essaouira field was evaluated at ambient temperature using polarization curves and EIS that were associated with SEM and EDAX techniques. The following points give the most important remarks that can be concluded from this research:
  • - Polarization resistance Rp of all samples increase with the immersion time in sandy soil. This is assigned to the formation of a protective film on the surface of each electrode. This protective film is related to the chemical composition of alloys such as Cu, Zn, P, As and Sn which transformed to the oxide film.

  • - Rs was found to increase with the immersion time; this increase could be related to the soil which becomes less conductive due to the Cl and SO42− ions concentration decrease. As a matter of fact, Chloride ions tend to dissolve many metals specially at acidic pH. Besides, the soil resistivity also decreases because of their concentration.

  • - The corrosion rate of the copper is less than 3 and 4 times in comparison with the bronze and brass, respectively.

  • - All measurements concluded that the possible corrosion of the studied materials can be classified in this order:

  • - SEM for the surface of the studied materials after 130 d of immersion revealed that a corrosion layer was formed with density dependence on the metal type.

The results that are obtained by EDAX and scanning electron microscopy are in agreement with those of the polarization and impedance measurements.


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Fig. 1
Electrochemical system designed for the study of copper alloy in Essaouira soil.
Fig. 2
Electrical equivalent circuit used for modeling the interface of (a) brass (b) copper (c) bronze / Essaouira soil with 20% of moisture.
Fig. 3
Nyquist (a) and Bode (b) diagrams for brass in Essaouira soil with 20% of moisture content at different immersion times.
Fig. 4
Nyquist (a) and Bode (b) diagrams for bronze in Essaouira soil with 20% of moisture content at different immersion times.
Fig. 5
Nyquist (a) and Bode (b) diagrams for copper in Essaouira soil with 20% of moisture content at different immersion times.
Fig. 6
Polarization curves for different electrode after 21 d of immersion in Essaouira soil with 20% of moisture content.
Fig. 7
Comparison of experimental (scatter) and fitting (red line) data using a nonlinear fitting with Stern-Geary equation for different electrode after 21 d of immersion in Essaouira soil with 20% of moisture content.
Fig. 8
SEM analysis microanalysis of the corroded surface after 130 d of immersion in sandy soil Essaouira at 20% of moisture content for bronze.
Fig. 9
SEM analysis microanalysis of the corroded surface after 130 d of immersion in sandy soil Essaouira at 20% of moisture content for brass.
Fig. 10
SEM analysis microanalysis of the corroded surface after 130 d of immersion in sandy soil Essaouira at 20% of moisture content for copper.
Table 1
Main features of Essaouira Soil As Received from the Field and Properties of the Soils
Concentration of various ions in aqueous extract (mg/L)
Ca2+ Mg2+ Cl SO42− Na+ K+
36 15.6 68.7 61.5 52.67 19.9
Essaouirasoil texture
Clay Silt Sand pH Moisture(%wt) CE(mS/cm)
8.3 13.6 78.1 6.85 ± 0.2 20 0.548
Table 2
Chemical Compositions of Different Electrodes with Addition Element
Copper alloys Composition, wt. %

α phase Cu Zn Pb Sn Fe Al Ni As Mn P Si Sb
Brass 91.27 70 21.95 1.27 0.57 1.71 3.675 0.45 0.010 0.1365 0.00165 0.0345 0.03
Bronze - 85.224 5.05 3.88 4.875 0.0615 - 0.705 0.016 - 0.01 - 0.099
Copper - 99.976 0.0031 0.0022 0.0022 - 0.0054 - - 0.0008 - -
Table 3
Electrochemical Impedance Parameters of All Electrode in Essaouira Soil with 20% of Moisture Content at Different Immersion Times
Parameters Brass Bronze Copper

1* 10* 15* 21* 1* 10* 15* 21* 1* 10* 15* 21*
Rs(Ω cm2) 40 43 45 50 75 81 84 92 48 50 51 50
Qf(μF cm−2) 294 310 236 312 111 395 98 76 450 126 280 240
αf 0.71 0.73 0.74 0.71 0.72 0.72 0.74 0.78 0.61 0.94 0.95 0.95
Rf(Ω cm2) 1,088 2,201 2,309 2,518 713 380 6,577 6,950 20 70 165 840
Qct(μF cm−2) 61 93 57 49 314 306 297 95 174 141 130 121
αct 1 1 1 0.97 1 1 0.72 0.78 0.57 0.73 0.73 0.77
Rct(Ω cm2) 3,122 3,067 3,183 3,350 5,672 9,169 9,681 12,450 1,226 1,828 3,265 2,508
S(Ω s−1/2) - - - - 26 221 75 50 - - - -
Qdif(μF cm−2) - - - - - - - - 166 124 123 121
αdif - - - - - - - - 0.66 0.66 0.67 0.64
Rdif/(Ω cm2) - - - - - - - - 10,392 14,809 22,852 30,410
Rp(Ω cm2) 4,209 5,268 5,492 5,868 5,672 9,169 16,258 19,310 11,618 16,637 26,117 32,919

time in days

Table 4
Polarization Curves Parameters for Different Electrode after 21 Days of Immersion in Essaouira Soil with 20% of Moisture Content
Brass grad Ecorr (mV/Cu/CuSO4) Tafel plot (1/mV) Icorr (μA/cm2)
βa −βc
SMCV −311 21.77 15.68 10.3
Bronze −278 12.12 4.35 6.8
Copper −239 12.23 9.4 2.3
Table 5
The Composition of the Corrosion Layer Formed on Surface in Each Electrode After 130 Days of Immersion in Sandy Soil Essaouira at 20% of Moisture Content
Element/Weight/% Bronze Brass Copper
C 10.33 7.68 -
O 29.47 27.87 2.53
Na - 2.19 -
Mg 0.28 0.13 -
Al 0.21 4.48 -
Si 0.62 0.59 -
S 0.36 1.06 0.33
Cl 1.68 1.59 -
Ca 6.47 0.11 -
Mn - 0.12 -
Fe 0.16 2.52 -
Ni 0.69 0.40 -
Cu 33.15 35.69 97.13
Zn 4.48 14.88 -
Mo 0.00 - -
Sn 6.55 0.60 -
Pb 5.55 - -
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