This paper aims to examine the efficiency of 5-chlorobenzotriazole (5Cl-BTA) as a copper corrosion inhibitor in acidic rain solutions with a pH value of 2.42 by the electrochemical polarization method. 5-Chlorobenzotriazole acts similar to a mixed type inhibitor, according to the potentiodynamic polarization measurements. Results obtained in this research suggest that 5Cl-BTA is a good inhibitor; it decreases anodic and cathodic reaction rates, and the highest inhibition efficiency was 91.2%. The inhibitory effect of 5-chlorobenzotriazole is explained by the formation of the layer on the copper surface. Stability of the protective layer increased with inhibitor concentration. Scanning electron microscopy and energy-dispersive analysis of X-rays analysis confirmed that on the electrode surface, a protective layer was formed. Adsorption of 5Cl-BTA obeys the Langmuir adsorption isotherm. 5Cl-BTA showed good inhibitory characteristics even when the Cl- ions were present in examined solutions.
This paper aims to examine the efficiency of 5-chlorobenzotriazole (5Cl-BTA) as a copper corrosion inhibitor in acidic rain solutions with a pH value of 2.42 by the electrochemical polarization method. 5-Chlorobenzotriazole acts similar to a mixed type inhibitor, according to the potentiodynamic polarization measurements. Results obtained in this research suggest that 5Cl-BTA is a good inhibitor; it decreases anodic and cathodic reaction rates, and the highest inhibition efficiency was 91.2%. The inhibitory effect of 5-chlorobenzotriazole is explained by the formation of the layer on the copper surface. Stability of the protective layer increased with inhibitor concentration. Scanning electron microscopy and energy-dispersive analysis of X-rays analysis confirmed that on the electrode surface, a protective layer was formed. Adsorption of 5Cl-BTA obeys the Langmuir adsorption isotherm. 5Cl-BTA showed good inhibitory characteristics even when the Cl- ions were present in examined solutions.
Copper is different
from most of the other
metals in that it combines corrosion resistance and electrical and
heat conductivity. It is a relatively noble element and that is the
reason it does not corrode readily in acids, unless some oxidizing
agents or oxygen is present. Copper owes its nobility to the formation
of a passive oxide film on its surface or other insoluble corrosion
products.[1]Several studies deal with
copper and copper alloy decay under different climatic conditions,
both natural and artificial. To understand the degradation processes
is very important for restoration purposes.[2] To protect metals and alloy surfaces from corrosion caused by the
attack of atmospheric corrosion (acid rains), suitable inhibitors
can be applied.Copper corrosion is highly dependent on the
composition of the electrolyte, which is in contact with the metal
surface. The process of copper corrosion includes copper dissolution
at local anodic sites and the electrochemical reduction of some species,
for example, oxygen at the cathodic area.[3] When Cl– ions are present in the experimental
solution, it leads to creating sites that are more liable for the
corrosion.In order to protect the metal surface in aggressive
environments, various, mainly organic, substances are used, and they
block reactive sites on the copper surface. Based on previous research,
the most effective corrosion inhibitors are the organic molecules
consisting of a π-system and/or containing atoms such as nitrogen,
oxygen, or sulfur in their molecule structures as well as molecules
with high molecular mass.[4−7] Many
investigations showed that especially good inhibitory effect on copper
and its alloys had amino acids,[8,9] imidazoles,[10,11] benzotriazole and its derivatives[12] and
many others. Among them, benzotriazole is particularly distinguished.
Using the organic inhibitors to protect metals from corrosion is one
of the most important methods in the corrosion protection. The inhibition
mechanism can take place through two processes: formation of a protective
thin layer via inhibitor adsorption or the formation of a precipitate
of the inhibitor on the metal surface.[13] The mechanism of action of the organic corrosion inhibitors is usually
not known. However, it is generally accepted that the inhibition of
corrosion is achieved thanks to the interaction between corrosion
inhibitor molecules and the metal surface. This leads to the formation
of the inhibitive film on the metal surface.[7]Although benzotriazole has been shown to have excellent inhibitory
properties in alkaline and neutral environments, in acidic environments,
the efficiency has been shown to decline.[8] However, BTA still showed great results in various media and on
different metals and alloys even at different temperatures.[14−16]Benzotriazole and its derivatives
were investigated as inhibitors of metal corrosion and are the most
commonly used N-containing compound. From the literature data it can
be observed that benzotriazole is more efficient for copper and its
alloys than for other metals. This was the reason to examine 5-chlorobenzotriazole
in various concentrations in acid rain solution pH 2.42 and in the
presence of chloride ions, based on electrochemical methods, quantum
chemical calculations, and scanning electron microscopy (SEM) and
energy dispersive analysis (EDS) of X-rays.
Result and Discussion
The open circuit potential (OCP)
values of the copper electrode in acid rain solution and in solutions
with different concentrations of the inhibitor were recorded for 30
min. Results are shown in Figure a,b. Obtained results showed that the curve recorded
in basic solution shifts toward more positive values at the end of
the immersion period. In the presence of 5-chlorobenzotriazole, the
values of OCP were shifted to the positive direction at the end of
measurement in comparison to the blank solution. This behavior could
be due to the fact that the adsorption of 5Cl-BTA occurs on the active
sites of the copper electrode, which leads to the inhibition of copper
electrode corrosion.[17] According to the
results, the shift of the OCP is lower than 85 mV, and it can be proposed
that 5Cl-BTA acts as a mixed-type inhibitor.[18]
Figure 1
OCP of a copper electrode
(a) in acid rain solution (pH 2.42) with and without 5-chlorobenzotriazole
and (b) with the addition of 0.05 mol/dm3 NaCl in acid
rain solution and the highest concentration of 5-chlorobenzotriazole,
for 30 min.
OCP of a copper electrode
(a) in acid rain solution (pH 2.42) with and without 5-chlorobenzotriazole
and (b) with the addition of 0.05 mol/dm3 NaCl in acid
rain solution and the highest concentration of 5-chlorobenzotriazole,
for 30 min.Results shown in Figure b showed evident dissolution of the copper electrode
in the presence of Cl– ions in basic acid rain solution.
Further, in the presence of the highest concentration of the 5-chlorobenzotriazole
value of OCP shifted to positive values because of the adsorption
of 5Cl-BTA on the active sites of the copper electrode.Cyclic
voltammograms were recorded in order to obtain more information about
the corrosion of copper in acid rain solution and in the presence
of 5Cl-BTA. Voltammograms are shown in Figure a and the results indicate that the presence
of different concentrations of the used inhibitor has the effect of
reducing the current density that is particularly pronounced at higher
concentrations. This phenomenon can be explained by the formation
of a protective film on the copper surface.
Figure 2
Cyclic voltammograms of copper electrode: (a)
in acid
rain solution and with the addition of different concentrations of
5-chlorobenzotriazole (b) and with the addition of 0.05 mol/dm3 NaCl in acid rain solution and the highest concentration
of 5-chlorobenzotriazole, scan rate 10 mV/s.
Cyclic voltammograms of copper electrode: (a)
in acid
rain solution and with the addition of different concentrations of
5-chlorobenzotriazole (b) and with the addition of 0.05 mol/dm3 NaCl in acid rain solution and the highest concentration
of 5-chlorobenzotriazole, scan rate 10 mV/s.According to the
literature, the initial step of the copper corrosion is the charge
transfer reaction, and this leads to the formation of an adsorbed
Cu+ species (Cuads+)[19]Therefore, from the reaction mechanism
(eq ), it can be concluded
that the copper electrode can produce cuprous ions in the H2SO4 solution containing air, on the basis of which it
can be assumed that 5Cl-BTA molecules form a coordination compound
with cuprous ion.[20] Cuads+ associate with an anion species X that diffuses from the bulk solution to the electrode surface(Cu+)X then diffuses into the bulk solutionThe cathodic reaction in acid solutions is
the reduction of oxygen, it can be described as oxygen diffusion from
the solution and adsorption on the surface of the electrodeIn the presence of oxygen, the cathodic
reaction is enhanced because of oxygen reduction, which leads to copper
corrosion rapidly and forming of a porous oxide film, which is in
good electrical contact with the underlying metal[19,21,22]Anodic dissolution of copper in acid
media follows the proposed mechanismUnlike the two-electron electrodissolution
mechanism, copper in the presence of 5Cl-BTA electrooxidized primarily
to Cu+ and is able to form slightly soluble [Cu(I)–(Inh)]ads complexes as the main electrooxidation products in the
presence of a clean surface. Equations and 9 present the dissolution
of copper in acid rain solution, but in the presence of 5Cl-BTA, this
may participate in the forming of adsorbed [Cu(I)–(Inh)]ads complexes, according to the eq .[23] It was proposed
that the growth of the [Cu(I)–(Inh)]ads film is
controlled by the transport of Cu+ ions from the matrix
copper metal through the surface where the inhibitor molecules are
adsorbed. Initial adsorption of the 5Cl-BTA molecules and the positively
charged surface, followed by the formation of an insoluble polymeric
complex on the electrode surface. Change in the parameters such as
the exposure time, pH value, temperature, or 5Cl-BTA concentration
did not affect the structure of the [Cu(I)–(Inh)]ads complex. Taking into account that when pH < 3.5 Cu2O is unstable than thick acicular [Cu(I)–Inh]ads, crystallites grew on the surface. The formed surface film act as
a physical barrier to the aggressive ions.[24]The inhibition mechanism can be presented by the following
reactionTaking into account that 5-clorobenzotriazole
contains N atoms in its structure, they could be proposed as centers
of adsorption on the copper electrode surface, allowing the formation
of N–Cu chemical bond.[25]Literature
survey showed that when the Cu(I)–BTA complex was forming,
some discrepancies existed between the authors about the nature of
the interaction and the possibility of π bonding. Some authors
proposed a polymeric structure in a σ-bonded Cu(I)triazole model,
but some other authors suggested a model involving d–p bonding
between Cu(I) and the triazole ring. Recent studies showed that d–p
bonding probably represents only a minor contribution to the bonding
between Cu(I) and the benzotriazole anion because Cu is chemically
more noble and have d-bent completely full. Kovačević
and Kokalj[26] had reported that benzotriazole
bonds weakly on the copper surface with unsaturated N atom(s) through
σ-molecular orbitals. Considering other compounds that act similar
to copper corrosion inhibitors and which are characterized by a chemical
structure similar to benzotriazole (5-chlorobenzotriazole), it can
be assumed that they also protect copper by forming complexes as well
as benzotriazole.[27] Because the 5Cl-BTA
is neutral in slightly acidic solution, according to the literature,
it could be said that the formed complex on the Cu surface is polymeric
with a linear structure, in which copper was bonded by coordination
involving a lone pair of electrons from one nitrogen atom and a covalent
link formed by the replacement of the H atom from the N–H group.Moreover, substituted BTAH derivatives were found to be effective
Cu corrosion inhibitors when functional groups are present on the
benzene ring, but not the triazole ring such as 5Cl-BTA.[24]According to reaction , the protective complex was formed, but
at potential values more positive than 0.25 V versus SCE, the current
density increases. This is probably due to the oxidation of the formed
layer on the electrode surface.[28] In the
reverse scan direction, the cathodic peak at potential ∼−0.220
V versus SCE is noticed and represents the reduction of copper ions.[29]Figure a also showed that in the positive sweep, pitting corrosion
occurs. Literature data indicate that pitting corrosion occurs when
there is a sudden increase in the current density and when the reverse
current density is greater in the reverse sweep than in the positive
sweep in the anodic region. The continuous growth of pits on the electrode
surface that occurs in the blank solution and in solutions with inhibitor,
but on more positive potential values, can be the reason for this
noticed current increase.[30]When
chloride ions in the concentration of 0.05 mol/dm3 NaCl
(Figure b) were present
in the acid rain solution, a sharp increase of the current density
at lower values of potentials is evident. Also, when the inhibitor
with concentration of 1 × 10–3 mol/dm3 was present in the solution, the current density had the same trend,
but the inhibitory effect of benzotriazole derivate was evident. The
presence of the chloride ions in the examined solutions lead to the
formation of the CuCl species layer on the copper surface.[31] These species are unstable in an acidic environment.
Also, CuCl species in the presence of Cu+ ions are easily
converted into a soluble CuCl2– complex,
and this is evident on cyclic voltammograms as a sharp increase in
current density values. The following reactions fit the described
mechanism[32,33]The reduction that occurs in the reverse
sweep can be ascribed to the reduction of the soluble CuCl2– complex and CuCl layer reduction on the copper
surface.[34,35] The presence of the inhibitor decreases
the reduction peak intensity, which indicates the inhibitory effect
of 5Cl-benzotriazole.Electrochemical corrosion parameters were
obtained by potentiodynamic polarization curves, which are shown in Figure a,b. All potentiodynamic
measurements are carried out after the OCP measurements. From Figure a, it could be noted
that the addition of 5-chlorobenzotriazole leads to the decrease of
the current density at all applied concentrations compared to the
blank solution. Increase of the inhibitor concentration decreases
the current density value. This leads to the conclusion that 5Cl-BTA
is adsorbed on the electrode surface and hinders both cathodic and
anodic reactions. The displacement of Ecorr is less than 85 mV, and the inhibitor can be characterized as a
mixed type of inhibitor,[18] although the
displacement is toward more positive values with the addition of the
inhibitor.
Figure 3
Linear voltammetric
curves
of copper (a) in acid rains solution and in the presence of various
concentrations of 5-chlorobenzotriazole, (b) in acid rain solution
in the presence of 5-chlorobezotriazole and with the addition of 0.05
mol/dm3 NaCl, scan rate 1 mV/s.
Linear voltammetric
curves
of copper (a) in acid rains solution and in the presence of various
concentrations of 5-chlorobenzotriazole, (b) in acid rain solution
in the presence of 5-chlorobezotriazole and with the addition of 0.05
mol/dm3 NaCl, scan rate 1 mV/s.From Figure a, it can be seen that in the blank solution, a small cathodic
current peak appeared at approximately −0.06 V versus SCE.
This peak can be ascribed to the process of reduction of cupric corrosion
products formed during the waiting time at Ecorr and remaining at the electrode surface.[36,37] Polarization
curves of the anodic branch showed that the slope of the anodic polarization
curve increases sharply on more positive potential values. The gradual
desorption of 5Cl-BTA molecules occurs and the anodic current density
remarkably increases. Therefore, the formation of the anchored adsorption
film of the used inhibitor exhibits an active blocking effect.[20,38]When Cl– ions were present in the acid rain
solution (Figure b),
the anodic curves for copper are in agreement with the Tafelian behavior
and simultaneous inhibition of both the anodic and cathodic reactions
occurs. In Figure b, the cathodic current peak, which was appeared at approximately
−0.217 V versus SCE is evident and could be explained by the
reduction of cupric species, which were formed during the waiting
time at Ecorr and remained at the copper
surface.[37]The electrochemical parameters
of copper corrosion in acid rain solution: corrosion potential (Ecorr), corrosion current density (jcorr), anodic (ba) and cathodic
(bc) Tafel slopes, and inhibition efficiency
(IE) are calculated from potentiodynamic curves and presented in Table . The jcorr and Ecorr parameters
were calculated from anodic and cathodic Tafel lines in the vicinity
of the linearized current regions.[39] The
inhibition efficiency was calculated according to the following equationwhere jcorr and jinh are corrosion
current densities for basic solution of acid rains and with the addition
of 5-chlorobenzotriazole.
Table 1
Electrochemical Parameters and Inhibition
Efficiency
of Copper Electrode in Acid Rain Solution and with the Addition of
Different Concentrations of the Inhibitor and with NaCl
inhibitor, mol/dm3
Ecorr, V vs SCE
jcorr, μA/cm2
ba, V/dec
–bc, V/dec
IE, %
AR
–0.025
5.89
0.049
0.254
1 × 10–3
0.039
0.51
0.036
0.076
91.2
5 × 10–4
0.028
0.57
0.052
0.154
90.2
1 × 10–4
0.014
0.91
0.079
0.257
84.4
5 × 10–5
0.008
0.97
0.075
0.205
83.4
AR + NaCl
–0.060
8.60
0.045
0.113
1 × 10–3 + NaCl
–0.053
0.70
0.033
0.183
91.8
Electrochemical
Impedance Spetroscopy
In order to examine in more detail
the influence of the 5Cl-benzotriazole on the electrochemical behavior
of copper in acid rain solution, electrochemical impedance spectroscopy
(EIS) was applied. The obtained results are shown in Figure . According to data shown in Figure , EIS parameters
were obtained by fitting and can be seen in Table . It is observed
by
analyzing the Nyquist diagram that the semicircle diameter increases
when in blank solution was added 1 × 10–3 mol/dm3 5Cl-BTA, indicating a decrease in corrosion.[40] Additionally, the appearance of Warburg impedance at a
low frequency region, points to that the corrosion process is controlled
by mixed charge-transfer and diffusion in solution,[40] that is, the diffusion of dissolved oxygen or some other
corrosive products on to the electrode surface[41] or the diffusion of soluble copper species.[42]
Figure 4
Nyquist plots
for copper
in acid rain solution and in the presence of 5Cl-benzotriazole.
Table 2
Impedance Parameters
Derived from Plots for Copper in Acid Rain Soultion and with the Addition
of 1 × 10–3 mol/dm3 5Cl-BTA
inhibitor, mol/dm3
Rs, Ω cm2
Rf, Ω cm2
Rct, Ω cm2
W, Ω–1 cm–2 s0.5
Cf, μF cm–2
n1
Cdl, μF cm–2
n2
IE, %
167.2
400.6
500.4
32
7.30 × 10–7
0.7279
3.82 × 10–6
0.665
1 × 10–3
176
8923
129.1
1660
5.16 × 10–8
0.857
1.08 × 10–6
0.71
90.05
Nyquist plots
for copper
in acid rain solution and in the presence of 5Cl-benzotriazole.The IVIUM soft program was used for fitting
experimental data, and the equivalent circuit is shown in Figure . From this equivalent
circuite, Rs represents solution resistance, Rf is the resistance of the protective inhibitor
film formed on the copper surface, and Rct is the charge transfer resistance. Qf and Qdl represent the constant phase
elements, Cf is film capacitance while Cdl is double-layer capacitance, W stands for Warburg impedance, and n for the deviation parameter.[43]
Figure 5
Electrical
equivalent circuit for copper in acid rain solution and 5Cl-benzotriazole.
Electrical
equivalent circuit for copper in acid rain solution and 5Cl-benzotriazole.The values of Cf and Cdl are calculated according to
the following equationsAccording to the data showed in the Table , it can be seen that the introduction of
an inhibitor in acid rain solution leads to decrease of Cf and Cdl values and Rct and Rf values
increase with the addition of 5Cl-BTA. Cf decreases because of the adsorption of the inhibitor on the copper
surface,[44] while decrease of Cdl corresponds to the increase of the electrical double
layer thickness and the decrease of the local dielectric constant
because of the adsorption of inhibitor molecules.[45]The Rf values are higher
when the inhibitor is present in solution indicating the formation
of the protective film and/or corrosion products on the copper surface.It is very important to highlight that the value of n increases
in the presence of 5Cl-BTA, which implys a decrease of the surface
inhomogeneity as a result of the inhibitor adsorption.[23]The inhibition efficiency is calculated
via equation[46]where R0p and Rp (Ω
cm2) stand for the resistance (Rp = Rf + Rct) of copper in acid rain solution without and with the addition of
5Cl-benzotriazole.
Quantum Chemical
Calculations
In order to determine the relationship between
some quantum chemical parameters gathered from the structure of the
inhibitor molecule (Figure ) and the inhibition efficiency of corrosion obtained by electrochemical
methods, the theoretical calculations were applied (Figure ). The inhibition property
of the inhibitor has been often correlated with the energy of HOMO
and LUMO and the HOMO–LUMO gap.[47]EHOMO (the highest occupied molecular
orbital energy), ELUMO (the lowest unoccupied
molecular orbital energy), ΔE (energy gap),
η (global hardness), σ (softness), μ (dipole moment),
ionization potential (I), electron affinity (A), χ (electronegativity), and ΔN (function of electron transferred from the inhibitor molecule to
the metal surface) were calculated.[48]
Figure 6
Structure
of the 5-chlorobenzotriazole molecule.
Figure 7
The proposed
spatial
distribution of HOMO and LUMO for 5-chlorobenzotriazole.
Structure
of the 5-chlorobenzotriazole molecule.The proposed
spatial
distribution of HOMO and LUMO for 5-chlorobenzotriazole.All calculated parameters are given in Table . Calculated quantum chemical parameters
were obtained by the following equations
Table 3
Quantum Chemical
Parameters
parameters
5Cl-BTA
EHOMO, eV
–9.9580
ELUMO, eV
–3.6716
ΔE, eV
6.2864
I, eV
9.9580
A, eV
3.6716
χ, eV
6.8148
η, eV
3.1432
ΔN
–0.371
μ, D
3.7439
The absolute chemical
hardness is given byand absolute electronegativity is given byThe fraction of electrons transferred between
the inhibitor molecule and the metal surface can be presented as[49]where χmatal and χmolecule are absolute electronegativity of
copper (metal) and the inhibitor molecule, respectively; ηmetal and ηmolecule are absolute hardness
of metal and the inhibitor molecule, respectively. Theoretical values
of χmatal and ηmetal for copper
are 4.48 and 0 eV/mol, respectively.[47]The value of ELUMO indicate the ability
of a molecule to accept electrons, and hence, to be adsorbed on the
metal surface, the values of EHOMO represent
the ability of molecule to donate electrons and subsequently have
better adsorption and inhibition efficiency.[50] Increasing values of EHOMO facilitate
adsorption and therefore enhance the inhibition efficiency by influencing
the transport process through the adsorbed layer.[47] The low values of ΔE corresponds
to a higher corrosion inhibition efficiency,[51] also small value of η shows that it reacts with the surface
more readily and the corrosion effect decreases, and on the other
hand great μ facilitates interaction with the metal surface.
Similar observations are already presented in the literature.[52,53] Parameter ΔN, also known as electron-donating
ability, evaluates the tendency of a molecule to donate electrons
to the metal surface, and the inhibition efficiency increases by increasing
the electron-donating ability of the inhibitor to donate electrons
to the metal.[48]
SEM and EDS of Copper
In order to observe the morphology
of the copper surface in acid rain solution pH 2.42 and in the presence
of 1 × 10–3 mol/dm35-chlorobenzotriazole
with the addition of 0.05 mol/dm3 NaCl, the SEM was applied.
In addition, for the determination of the elements present on the
copper surface, in uninhibited solution, and in inhibited solution,
EDS technique was applied. According to Figure , it is evident that copper in acid rain
solution was degradedbecause of metal dissolution in aggressive media.
However, when the inhibitor was present in the blank solution (Figure ), the surface of
copper was relatively smoother. This behavior can be explained by
the adsorption of 5-chlorobenzotriazole on the copper surface and
inhibition of the copper corrosion. From Figure it can be observed that the copper surface
was strongly damaged as a result of the addition of Cl– ions in the blank solution of acid rains. Nevertheless, with the
addition of the inhibitor (Figure ) the copper surface was much smoother, which led to
a conclusion that the inhibitor was adsorbed on the metal surface.
Figure 8
SEM image and
EDS spectrum of the copper surface after 48 h in acid rains solution.
Figure 9
SEM image
and EDS spectrum of the copper surface after 48 h in 1 × 10–3 mol/dm3 5-chlorobenzotriazole solution.
Figure 10
SEM
image and EDS spectrum of the copper surface after 48 h in acid rain
solution with the addition of 0.05 mol/dm3 NaCl.
Figure 11
SEM
image and EDS spectrum of the copper surface after 48 h in 1 ×
10–3 mol/dm3 5-chlorobenzotriazole solution
with the addition of 0.05 mol/dm3 NaCl.
SEM image and
EDS spectrum of the copper surface after 48 h in acid rains solution.SEM image
and EDS spectrum of the copper surface after 48 h in 1 × 10–3 mol/dm35-chlorobenzotriazole solution.SEM
image and EDS spectrum of the copper surface after 48 h in acid rain
solution with the addition of 0.05 mol/dm3 NaCl.SEM
image and EDS spectrum of the copper surface after 48 h in 1 ×
10–3 mol/dm35-chlorobenzotriazole solution
with the addition of 0.05 mol/dm3 NaCl.Conducted EDS analysis of the copper surface after immersion in
acid rain solution (pH 2.42) detected Cu and O peaks (Figure ), so it could be concluded
that copper corrosion products, such as Cu2O and CuO, were
formed.[54] When the inhibitor was added
to the basic solution, in concentration of 1 × 10–3 mol/dm3 (Figure ), at the EDS spectrum C peak, which was derived from the
organic inhibitor, was also detected beside the Cu and O peaks. Upon
the addition of NaCl in acid rain solution, except Cu and O peaks,
the EDS spectrum (Figure ) showed Cl peak as a consequence of the soluble Cl2– complex and CuCl layer on the copper surface. Figure shows the EDS
analysis for copper in acid rain solution with the presence of the
inhibitor and NaCl and beside Cu, O, and Cl peaks, N peak, which was
derived from 5-chlorobenzotriazole, is also detected. SEM figures
and EDS spectra proved that 5-chlorobenzotriazole could be used as
a copper corrosion inhibitor in acid rain solution, pH 2.42 and when
Cl– ions are present in solution as well. These
results are in agreement with the electrochemical measurements.
Adsorption Isotherm
The adsorption
of the inhibitor on the electrode surface could be observed as the
adsorption of 5-chlorobenzotriazole at the copper solution interface
and the substitution process between the organic compound (orgsol) from the aqueous medium and the water molecules associated
with the metal surface (H2Oads)where “x” is the number of water molecules
replaced by the adsorption of one 5-chlorobenzotriazole molecule.[55]According to the type of the forces, adsorption
can be physisorption, chemisorption, or a combination of both.[29] Literature data showed that if the values of
−ΔG are 20 kJ/mol or lower physisorption
occurs, but when the values are above 40 kJ/mol charge, sharing or
transfer from the inhibitor molecules to the metal surface to form
a coordinate type of bond is involved.[56]The Langmuir adsorption isotherm was tested as an adsorption
model, which can be presented in the following waywhere Kads is the equilibrium constant for the adsorption/desorption
process and Cinh is the inhibitor concentration.[57]Gibbs free energy of adsorption was calculated
according to the equationwhere R stands for the universal gas constant (J/Kmol)
and T is the thermodynamic temperature (295 K).A linear relation (R2 = 0.9999) between
the Cinh/θ and Cinh (Figure ) points to the adsorption of 5Cl-BTA on the copper surface
obeys the Langmuir adsorption isotherm. Based on data obtained from Figure (Kads = 7.67 × 10–6) and according
to the previous equation, Gibbs free energy of adsorption was calculated
−38.5 kJ/mol and leads to the conclusion that strong adsorption
of inhibitor molecules on the electrode surface appeared.[58]
Figure 12
Langmuir
adsorption isotherm of 5-chlorobenzotriazole on the copper surface.
Langmuir
adsorption isotherm of 5-chlorobenzotriazole on the copper surface.
Conclusions
5-Chlorobenzotriazole
acts as a good copper corrosion inhibitor
in acid rain solution pH 2.42, with the highest inhibition efficiency
of 91.2%. The potentiodynamic polarization measurements indicated
that this organic molecule acts as a mixed type of inhibitor. The
inhibitory effect and adsorption of 5Cl-BTA were confirmed by SEM
and EDS. The adsorption of 5-chlorobenzotriazole obeys the Langmuir
adsorption isotherm. Gibbs free energy of adsorption was calculated
−38.5 kJ/mol and leads to the conclusion that adsorption of
inhibitor molecules on the electrode surface was spontaneous.
Experimental
Section
All electrochemical
tests of the copper behavior were conducted in acid rain solution
(AR) pH 2.42, with or without the addition of the 5Cl-benzotriazole
(Aldrich) (concentration 1 × 10–3, 5 ×
10–4, 1 × 10–4, 5 ×
10–5 mol/dm3). The basic acid rains solution
consisted of: 0.2 g/L Na2SO4 (Alkaloid Skopje),
0.2 g/L NaHCO3 (Hemos), 0.2 g/L NaNO3 (Merck),
and distillated water. The pH value of the basic solution was adjusted
by adding H2SO4. Chloride ions in the form NaCl
were added to the blank acid rain solution and solution containing
1 × 10–3 mol/dm3Cl-BTA. Potentiostat
(Ivium XRE, Ivium Technologies) with corresponding software was used
for testing. The working electrode was made of copper with an area
of 0.49 cm2. This electrode was prepared from a copper
wire, which was cut and sealed with epoxy resin. Before each measurement,
the copper electrode was polished with emery paper (Al2O3 with SiO4) and 0.3 μm grit alumina
paste (Buehler USA). Measurements were made in a three-electrode system
with the saturated calomel electrode (SCE) as reference and the platinum
electrode was the auxiliary one. The following methods were used:
measuring of the OCP for 30 min, linear voltammetry, cyclic voltammetry,
SEM and EDS, and quantum chemical calculations. Linear voltammetry
was recorded from the OCP to ±0.300 V versus SCE in both cathodic
and anodic directions at a scan rate of 1 mV/s. Cyclic voltammetry
was conducted in the potential range from −1.000 to −1.000
V versus SCE with a scan rate of 10 mV/s. All measurements were performed
at room temperature (298 K) in naturally aerated solutions. The potential
is expressed referring to a saturated calomel electrode. The SEM–EDS
measurements were conducted using the Tescan VEGA 3 LM scanning electron
microscope equipped with the Oxford EDS X-act Inca 350 system. Quantum
chemical calculations and molecule geometry optimization were performed
using ArgusLab 4.0, software. This software was already proven useful
for similar investigations. The PM3-SCF method was applied. The geometry
of the inhibitor in its ground state, as well as the nature of their
molecular orbital, the HOMO, and the LUMO are the properties influencing
the activity of inhibitors.EIS measurements were performed
at OCP. The frequency range was of 100 kHz to 10 mHz with an amplitude
of 10 mV peak to peak using IVIUM soft.