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IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
_______________________________________________________________________________________________
Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 382
EFFECTS OF ANION ON THE CORROSION BEHAVIORS OF
CARBON STEEL UNDER ARTIFICIAL RAIN FALL TEST
Dara TO1, Tadashi Shinohara2, Osamu Umezawa3
1
Material Reliability Unit, National Institute for Material Science (NIMS), Tsukuba 305-0047, JAPAN, & Graduate
School of Engineering, Yokohama National University (YNU), Yokohama 240-8501, JAPAN
2
Material Reliability Unit, National Institute for Material Science (NIMS), Tsukuba 305-0047, JAPAN
3
Graduate School of Engineering, Yokohama National University (YNU), Yokohama 240-8501, JAPAN
Abstract
Rain is one of the main importance issues for atmospheric corrosion problem. Effects of rainfall on corrosion behaviors of carbon
steels were investigated using artificial rainfall equipment. Three types of Atmospheric Corrosion Monitoring (ACM) sensors,
which consist of Fe-Ag, Zn-Ag, and Al-Ag galvanic couples, were used to illustrate the correlation between the sensors output,
Corrosion Rate (CR), and chemical concentration in the rain. The effects of ionic species on the corrosion behaviors were
observed by using NaCl, KCl, Na2SO4, NaNO3, and KNO3 as rainfall solutions. The result revealed that the rainfall rate was
insensitive to ACM sensors outputs and CRs. In contrast, the chemical species and their concentrations in the rainfall solution
significantly affected the ACM outputsand CRs. The corrosivity of the cations (Na+
and K+
) is negligible compared to the anions
(Cl-
, SO4
2-
, NO3
-
).For a given number of molar concentration, the CRs resulted from the corrosivity of SO4
-2
anions were higher
than that of Cl-
and NO3
-
anions,respectively. According to the empirical data, the CRs is increased and then reach a steady state
as the molar concentration iscontinuously increased.This research also indicates that the ACM sensors outputs of Fe-Ag and Zn-
Ag couples are capable of estimating corrosivity of the atmosphere, while the ACM sensor of Al-Agcouple can be used to
determine not only the time of wetness but also the typeofchemical species in the environment. The research methods discussed in
this paper proves that the CRs are dependent on the atmospheric composition and can be forecasted through ACM sensors.
Keywords: Corrosion Rate (CR), Atmospheric Corrosion, Air Pollution, Atmospheric Corrosion Monitoring (ACM)
Sensor, Sodium Chloride (NaCl), Sodium Sulfate (Na2SO4), Sodium Nitrate (NaNO3), Potassium Chloride (KCl),
Potassium Nitrate (KNO3).
--------------------------------------------------------------------***----------------------------------------------------------------------
1. INTRODUCTION
An environmental effect, such as corrosion attack, is the
most important factor for the design of metallic structure
like infrastructures, automotive, and other equipment, which
usually exposed to an outdoor environment. Atmospheric
corrosion is a very complicated process that causes
deterioration of metallic materials by chemical or
electrochemical reaction between the metal and its
environment. The Relative Humidity (RH), time of wetness
and numerous pollutant substances which involve species
deposited from atmosphere and species from the metal
resulting from corrosion itself affect to the atmospheric
corrosion [1].The atmospheric corrosions are often classified
into several qualitative zones, based on subjective
assessments of pollution factors, namely Rural, Urban,
Industrial, and Marine atmosphere [1-6]. Generally, therural
area is low corrosivity while Urban, Industrial, and Marine
atmosphere are, respectively, higher corrosivity due to the
existence of higher chemical contain in the atmosphere
[3,4]. The corrosive of marine area relates to the existence
of high Cl- concentrations in the atmosphere. Other chemical
species that can be found in the Urban and Industrial
atmospheres are SO2, CO2,and NO2, that product by gas
emission from the combustion engine [6-8]. Further
oxidation of SO2, usually in the presence of a catalyst such
as NO2, forms H2SO4, and thus, acid rain could initiate [8].
Atmospheric corrosion, depends mainly on air pollution, is
commonly initiates and develops under the thin water films,
the film which is considered as surface electrolyte layer,
formed by fog, dew, or raindrop. For a given time of
wetness (time during which the wet film exists), the greater
the pollution value, the greater the corrosivity formation. To
know and elucidate the effect of the pollution on the
corrosion behaviors, it is necessary to identify the pollutant
substances, and likewise, the time of wetness should be
taken into account. In this research, the corrosion behaviors
of carbon steel affected by several types of ionic species
were investigated by simulating artificial rainfall test. Three
type of ACM sensors were used to create the empirical data
for estimating the relation between sensor outputs and CRs.
The chemical species and its concentration in the rainfall
solution were taken as the main parameters of corrosion.
2. EXPERIMENTAL PROCEDURE
2.1 Chemical Composition in Rainfall Solution
Chemical properties, pH values, and electrical conductivities
of actual rain at National Institute for Material Science
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
_______________________________________________________________________________________________
Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 383
(NIMS), Tsukuba, Japan, were analyzed. The measurement
results show that the highest chemical concentration is
HCO3
- and follow by NO3
-, SO4
-
, and Cl- (as seen in Table
(1)). The pH value and electrical conductivities are about 4.8
~5.7 and 10~43 µs/cm respectively. In general, SO4
-
, Cl-, and
NO3
- are the most aggressive ionic species for corrosion
acceleration [1, 2]. In this experiment, NaCl, KCl, Na2SO4,
NaNO3, and KNO3 species, which are the major contain in
the actual rain, were mixed with Deionized water and used
as artificial rainfall solution.
2.2 Artificial Rainfall Equipment
The artificial rainfall equipment, as seen in Fig. 1, composed
of a chamber, a water reservoir, an air-compressor-mixer,
ACM sensors which are connected to a Data logger, and a
nozzle spray which is installed on the top of the chamber.
The rainfall distribution is considerably uniform, and it can
be adjusted to get a wide range of rainfall rate: 0.5 mm/h to
10 mm/h. However, the results of this experiment show that
the rainfall rate, H (mm/h), is insensitive to the CRs and
ACM sensors outputs. Hence, H= 1 mm/h was used for all
cases.
Table-1: Chemical properties in actual rainwater [9]
Date 06-Jun 07-Jul
25-Jul
Beginning Main
pH (24 C) 5.5 4.8 5.2 5.7
Conductivity
(µs/cm)
10 26 43 11
Concentration (mg/L)
Cl- 0.7 0.6 2.4 0.7
SO4
2- 2.0 3.7 5.3 1.3
NO3
- 1.2 3.5 7.5 1.4
Na+ 0.3 0.5 2.0 0.4
K+ 0.3 0.7 2.3 0.7
Ca2+ <0.1 0.2 0.2 <0.1
Mg2+ <0.1 <0.1 <0.1 <0.1
HCO3
- <5.0 <5.0 <5.0 <5.0
(a) 3D representation (b) Schematic illustration
Fig-1: Artificial rainfall equipment
2.3 Atmospheric Corrosion Monitoring (ACM)
Sensor
It has been known that galvanic couple sensing probe was
used for dew detector [10] time-of-wetness meter [11], or
moisture sensor [12]. Further integrations and applications
of this type of sensor, which is called Atmospheric
Corrosion Monitoring (ACM) sensor, has been used to
predict the behaviors of corrosion under atmospheric
condition [13]. The schematic illustration of ACM sensor,
which consists of the Fe-Ag couple, is presented in the Fig.
2. The signal output, which can be called galvanic current,
range between nanoampere to milliampere, depends mainly
on the electrical conductivity of aqueous film formed by
dew or raindrop on the striped surface of the sensor, as seen
in Fig. 2 (b). And the signal outputs of the sensors are
recorded and collected every minute by 16 CH Data logger
SYRINX SAXM-50F. In this research, three types ACM
sensors, Fe-Ag, Zn-Ag, and Al-Ag, were used to investigate
the phenomenon of corrosion through the signal output of
ACM censors.
2.4 Exposure Test and Measurement
Low-carbon steel sheets, SPCC, were used as specimens and
exposed to the artificial rainfall by a limited and single face.
The backside, cut edge, and fringe of the specimens were
covered by polyethylene sheetin order to avoid undesired
corrosion occurs, as seen in Fig. 3. The ACM sensors and
specimens were installed at the bottom of the chamber and
incline 45o with a vertical plan. Each test was conducted 16
hours with two times repeated. The CRs were computed
based on weight loss method; the samples were immersed in
the Hydrochloric Acid (HCl) to remove the corrosion
products or rust layer, then weight-loss was measured
(ISO/DIS 8403.3 [14]).
Fig-2: Schematic illustration of Fe-Ag ACM sensor, (a)
overall view, (b) section view [13].
Aqueous
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
_______________________________________________________________________________________________
Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 384
Fig-3: Carbon steel sheet specimens, (a) Preparation the
specimen before exposure test, (b) After removing corrosion
product.
3. RESULTS
3.1 Molarity and Electrical Conductivity
The electric conductivity, σ (µs/cm), of all solutions linearly
increase with the increasing of molarity, c (mol/L), (Fig. 4).
In addition, Na2SO4 solutions present the highest electrical
conductivity while NaCl and NaNO3 solutions are
considerably similar trend line. It should be noted that the
relation between σ and c follow a general formula:
σ = β.c+ D (1)
Where β is the electricity coefficient and D is electrical
conductivity of deionize-water, in this experiment D ≈ 0.9 to
1.5 µs/cm.
Fig-4: The eclectically conductivity of Na2SO4, NaCl, and
NaNO3 solutions in function of molar concentration
3.2 Corrosion Rate Calculation
After removing corrosion product, or rust layer, from the
surface of the samples, weight loss was measured and
converted to thickness loss. The thickness loss per year is
called Corrosion Rate, CR (mm/y). The CR of the exposure
sample can be calculated according to the following
equation:
CR(mm/y) =
10 Wy
ρA
(2)
Where Wy is weight loss per year (g/y), ρ is the density of
carbon steel (7.86g/cm3), and A is the exposed area
(12.7×5.5cm2).
3.3 Effect of Rainfall Rate
The rainfall rates were insensitive to CRs and ACM sensors
outputs as seen in Fig. 5. It can be explained by the fact that
the CR can approach maximum when the electrolytesurface
film covering the metal become very thin, below 56 µm
[1,9,15-17]. For the larger thickness of the film, especially
under the rainfall with homogenous concentration, the CRs
will stabilize at a constant value.
Fig -5: The effect of rainfall rate to the sensor output in
Na2SO4 solution with the concentration of 3×10-4 mol/L
3.4 Effect of Anions on Corrosion Rate
In water, NaCl for instance, the molecules will separate into
ions: Na+ (cation), and Cl- (anion). And likewise for KCl,
NaNO3, and KNO3: K+, Cl-, Na+, NO3
-. The negative
charge, called anion, is the most corrosive ion because it has
much more tendency to catch electron from the metal
surface. Consequently, the metal will oxidize by transferring
the electron to the anion and liberating metal ion from metal
the surface. Fig. 6 show CRs resulting from the effect of the
anion and the variation of molarity. Evidently, Fig. 6 (a) and
(b)indicate corrosion tendency depend on Cl- and NO3
-
respectively, while the effect of K+ and Na+ is negligible.
This Phenomenondoes not mean for all cation, especially H+
that has natural tendency to accept the electron from
metallic-solution interface.
(a)
σ = 187791c +0.9
σ = 115047c + 0.9
σ = 108788c + 0.9
1.E+0
1.E+1
1.E+2
1.E+3
1.E+4
1.E-5 1.E-4 1.E-3 1.E-2 1.E-1
σ(µs/cm)
Molarity, c (mol/L)
Na2SO4
NaCl
NaNO3
1.E-1
1.E+0
1.E+1
1.E+2
1.E+3
0 2 4 6 8 10
Sensoroutput,I(µA)
Rainfall rate, H (mm/h)
Fe-Ag Zn-Ag Al-Ag
0.01
0.1
1
10
1.E-5 1.E-4 1.E-3 1.E-2 1.E-1
CR(mm/y)
Molarity, c (mol/L)
KCl
NaCl
CR = 0.5 ±0.1 mm/y
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
_______________________________________________________________________________________________
Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 385
(b)
Fig-6: Effect of anion on corrosion rate, (a) the effect of Cl-
,(b) the effect of NO3
-
3.5 Relation between Corrosion Rate and Molarity
Fig. 7 shows the logarithmic scale representation of CR in
function of molar concentration. Each data point is the CR
mean value of two-time repeated tests with three samples.
As it can be seen, SO4
2- is the most aggressiveness anion,
and follow by Cl- and NO3
-, respectively. According to the
empirical data, the CR of Na2SO4 and NaCl indicate the
transition from corrosion acceleration to deceleration and
tend to reach a steady state when molarity is continuously
increased. In particular, the CR of NaNO3 is considerably
constant, CR ≈ 0.05 mm/y, for c < 3.10-3 mol/L, elsewhere,
c > 3.10-3, the CR rapidly raises up. For the smaller
concentration, c <3.10-5mol/L, all the CRs are
approximately similar and remain steady.
Fig-7: Corrosivity of carbon steel sheet corroded by
Na2SO4, NaCl, and NaNO3 solutions
3.6 Relation between Sensor Outputs and Molar
Concentration
Fig. 8 shows the relation between sensor outputs in function
of molar concentrations. The galvanic currents of the three
sensors increase with the increasing of molar concentrations,
except Al-Ag galvanic current in NaNO3 solution (see Fig 8
(c)) that considerably unchangeable when c> 10-4 mol/L. For
Fe-Ag and Zn-Ag sensor, the galvanic currents in the
Na2SO4 solutions are higher than those in NaCl and NaNO3
solutions, respectively (see Fig. 8 (a) and (b)). On the
contrary, the Al-Ag galvanic currents in Na2SO4 solutions
are lower than those in NaNO3 and NaCl solution (see Fig. 8
(c)).
(a)
(b)
(c)
Fig-8: Relation between molar concentration and sensor
outputs, (a) Fe-Ag galvanic couple, (b) Zn-Ag Galvanic
couple, and (c) Al-Ag galvanic couple.
0.01
0.1
1
1.E-5 1.E-4 1.E-3 1.E-2 1.E-1
CR(mm/y)
Molarity, c (mol/L)
NaNO3
KNO3
0.01
0.1
1
10
1.E-6 1.E-5 1.E-4 1.E-3 1.E-2 1.E-1
CR(mm/y)
Molarity, c (mol/L)
Na2SO4
NaCl
Na2NO3
1.E-2
1.E-1
1.E+0
1.E+1
1.E+2
1.E+3
1.E+4
1.E-5 1.E-4 1.E-3 1.E-2 1.E-1
I(µA)
c (mol/L)
Na2SO4
NaCl
NaNO3
0.1
1
10
100
1000
1.E-5 1.E-4 1.E-3 1.E-2 1.E-1
I(µA)
Molarirty, c (mol/L)
Na2SO4
NaCl
NaNO3
1.E-1
1.E+0
1.E+1
1.E+2
1.E+3
1.E+4
1.E-5 1.E-4 1.E-3 1.E-2 1.E-1
I(µA)
Molarity, c (mol/L)
Na2SO4
NaCl
NaNO3
Deionized water
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
_______________________________________________________________________________________________
Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 386
3.7 Relation between CR and Sensor Output
Recall that; the sensor output is a current of the galvanic
couple that highly depend on ionic species in the aqueous
film formed on the surface of ACM sensor. Fig. 9 (a), (b),
and (c) present the outputs of the three sensors, Fe-Ag, Zn-
Ag, and Al-Ag in function of CR. With Na2SO4, NaCl, and
NaNO3 solutions, the sensor outputs of Fe-Ag and Zn-Ag
couple are relatively similar and congregated as a curve, as
seen in Fig. 9 (a) and (b). Conversely, the outputs of Al-Ag
sensor are completely deviated by chemical species (Fig. 9
(c)). Additionally, Na2SO4solution is less sensitive to the Al-
Ag sensor output, while it is sensible to the Fe-Ag and Zn-
Ag.
(a)
(b)
(c)
Fig -9: Relation between sensor output and CR, (a) Fe-Ag,
(b) Zn-Ag, and (c) Al-Ag galvanic couple
4. DISCUSSION
Atmospheric corrosion is an electrochemical process which
can only proceed in the presence of an electrolyte film. It is,
therefore, to be considered as discontinuous process, where
the total corrosion loss, COR, in a given time or period is
determined by the time of wetness, twn, and the average of
corrosion rate, CR, during the each period, n, of
condensation[1]:
COR = ∑ twn . CRnn (3)
The calculation the time of wetness based on meteorological
data (by taking RH≥ 80% and T ≥ 0 0C) might not achieve
the exact time that makes corrosion possible. Thus, the
technical measurement method using ACM sensor exposure
to the actual environment is more preferable. Virtually, Fe-
Ag and/or Zn-Ag galvanic couples enable to estimate the
time of wetness, twn, and corrosion rate,CRn, through the
empirical data (see Fig. 9 (a) and (b)). Al-Ag couple,
however, is unable to forecast the CR in the unknown
pollution species, especially the mixed species in the
atmosphere, due to the inconsistent relation of I-CR in
different solutions (Fig 9 (c)). Nonetheless, the Al-Ag
enables to estimate the time of wetness based on the great
lifetime service. And also, it allowspredicting the chemical
species in the environment. For instance, if the CR is high,
and the Al-Ag sensor output is low, the SO4
2- ions is
assumed as the major contain in the solution or the
environment. It has to be noted that the service-life of Fe-Ag
galvanic sensor is much lower than those of Zn-Ag and Al-
Ag, respectively. The rust layer could be visually detected
on the striped surface of the Fe-Ag sensor after about 64
hours rain (see Fig. 10), and it results to the increasing of the
sensor output and decreasing the sensibility of the sensor.
Thus, it is recommended to change the sensor frequently
during the exposure test.
5. CONCLUSION
The experimental analysis of the corrosion behaviors under
the artificial rainfall investigation allows to conclude as
below:
- The rainfall rates were insensitive to ACM sensors
outputs and CRs. In contrast, the chemical species and
their concentrations in the rainfall solution significantly
affected the ACM outputs and the CRs.
- The corrosivity ofcations is negligible compared to
anions. For a certain of molar concentration, the most
aggressiveness ions are SO4
-, Cl-, and NO3,
respectively.
- For further increasing molar concentration, the CR
tends to reach a steady state at the maximum value of
CR = 2mm/y.
- The ACM sensors are capable of estimating the time of
wetness and aggressivity of atmosphere, and thus the
total corrosion loss could be estimated.
- The lifetime of Fe-Ag galvanic sensor is much shorter
than those of Zn-Ag, and Al-Ag respectively since the
rust layer visually appears after 64 hours rain; thus the
sensibility of the sensor would not performwell.
1.E-2
1.E-1
1.E+0
1.E+1
1.E+2
1.E+3
1.E+4
0.01 0.1 1 10
I(µA)
CR (mm/y)
Na2SO4
NaCl
NaNO3
1.E-1
1.E+0
1.E+1
1.E+2
1.E+3
0.01 0.1 1 10
I(µA)
CR (mm/y)
Na2SO4
NaCl
NaNO3
1.E-1
1.E+0
1.E+1
1.E+2
1.E+3
1.E+4
0.01 0.1 1 10
I(µA)
CR (mm/y)
Na2SO4
NaCl
NaNO3
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
_______________________________________________________________________________________________
Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 387
Fig-10: Overview of corroded sample after 16 hours rain
with NaCl 10-2 mol/L, and ACM sensor after 80 hours rain
REFERENCES
[1] F. Mansfeld: Applied Sciences, 203(Electrochemical
and Optical Techniques for the Study and Monitoring
of Metallic Corrosion, 1991) pp. 571-584.
[2] ISO 9223: Corrosion of metals and alloys, Corrosivity
of Atmospheres. Classification, (1992).
[3] D. de la Fuente, I. Díaz: Corrosion Science. 53 (2011)
pp. 604–617
[4] M. Morcillo B. Chico: Corrosion Science. 77 (2013)
pp. 6–24
[5] Sei J. Oha, D.C. Cookb: Corrosion Science 41 (1999)
pp. 1687-1702
[6] J. Morales, S. Martin-Krijerz: Corrosion Science 47
(2005) pp. 2005–2019
[7] S. Sudalma, P. Purwanto: Procedia Environmental
Sciences 23 ( 2015 ) pp. 247 – 252
[8] Jekti Prihatin, A. Duran Corebima, Ariffin, Abdul
Gofur, The effect of exposure of mulberry to acid rain
on the defects Cocoon of Bombyxmori L, Procedia
Environmental science 23 (2015) 186-191
[9] T. Shinohara: ISSN 0892-4228, Corrosion
Engineering, 63 (2014) pp. 86-92.
[10] P.J. Sereda: ASTM Bulletin, No. 228, (1958) pp. 53:
ibid., No.238. (1958) pp. 61; ibid., No. 246, (1960) pp.
47
[11] P.R. Grossman: “Atmospheric Factors Affecting
Corrosion of Metals,“ Ed. By S.K Conburn, p. 5,
ASTM STP 66 (1978).
[12] P.J. Sereda, S.G. Croll and H.F. Slade: “Atmospheric
Corrosion of Metal,” Ed. By S.W. Dean, Jr. and E.C
Rhea, p. 267, ASTM STP 767 (1982).
[13] S.i. Motoda, Y. Suzuki, T. Shinohara: Corrosion
Engineering. 43 (1994) pp. 583-594.
[14] ISO/DIS 8403.3: Metals and alloys. Procedures for
removal of corrosion products from corrosion test
specimens, 1985.
[15] M. Stratmann, H. Strecke: Corrosion Science. 30
(1990) pp. 715–734.
[16] A. Nishikata, Y. Ichihara: J. Electrochem. Soc. 144
(1997) pp. 1244–1252.
[17] T. Tsuru, A. Nishikata: Mater. Sci. Technol. A198
(1995) 161–168.
Fe-Ag Zn-Ag Al-Ag
Corroded samples 16h rain
Rust layer

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Effects of anion on the corrosion behaviors of carbon steel under artificial rain fall test

  • 1. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 _______________________________________________________________________________________________ Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 382 EFFECTS OF ANION ON THE CORROSION BEHAVIORS OF CARBON STEEL UNDER ARTIFICIAL RAIN FALL TEST Dara TO1, Tadashi Shinohara2, Osamu Umezawa3 1 Material Reliability Unit, National Institute for Material Science (NIMS), Tsukuba 305-0047, JAPAN, & Graduate School of Engineering, Yokohama National University (YNU), Yokohama 240-8501, JAPAN 2 Material Reliability Unit, National Institute for Material Science (NIMS), Tsukuba 305-0047, JAPAN 3 Graduate School of Engineering, Yokohama National University (YNU), Yokohama 240-8501, JAPAN Abstract Rain is one of the main importance issues for atmospheric corrosion problem. Effects of rainfall on corrosion behaviors of carbon steels were investigated using artificial rainfall equipment. Three types of Atmospheric Corrosion Monitoring (ACM) sensors, which consist of Fe-Ag, Zn-Ag, and Al-Ag galvanic couples, were used to illustrate the correlation between the sensors output, Corrosion Rate (CR), and chemical concentration in the rain. The effects of ionic species on the corrosion behaviors were observed by using NaCl, KCl, Na2SO4, NaNO3, and KNO3 as rainfall solutions. The result revealed that the rainfall rate was insensitive to ACM sensors outputs and CRs. In contrast, the chemical species and their concentrations in the rainfall solution significantly affected the ACM outputsand CRs. The corrosivity of the cations (Na+ and K+ ) is negligible compared to the anions (Cl- , SO4 2- , NO3 - ).For a given number of molar concentration, the CRs resulted from the corrosivity of SO4 -2 anions were higher than that of Cl- and NO3 - anions,respectively. According to the empirical data, the CRs is increased and then reach a steady state as the molar concentration iscontinuously increased.This research also indicates that the ACM sensors outputs of Fe-Ag and Zn- Ag couples are capable of estimating corrosivity of the atmosphere, while the ACM sensor of Al-Agcouple can be used to determine not only the time of wetness but also the typeofchemical species in the environment. The research methods discussed in this paper proves that the CRs are dependent on the atmospheric composition and can be forecasted through ACM sensors. Keywords: Corrosion Rate (CR), Atmospheric Corrosion, Air Pollution, Atmospheric Corrosion Monitoring (ACM) Sensor, Sodium Chloride (NaCl), Sodium Sulfate (Na2SO4), Sodium Nitrate (NaNO3), Potassium Chloride (KCl), Potassium Nitrate (KNO3). --------------------------------------------------------------------***---------------------------------------------------------------------- 1. INTRODUCTION An environmental effect, such as corrosion attack, is the most important factor for the design of metallic structure like infrastructures, automotive, and other equipment, which usually exposed to an outdoor environment. Atmospheric corrosion is a very complicated process that causes deterioration of metallic materials by chemical or electrochemical reaction between the metal and its environment. The Relative Humidity (RH), time of wetness and numerous pollutant substances which involve species deposited from atmosphere and species from the metal resulting from corrosion itself affect to the atmospheric corrosion [1].The atmospheric corrosions are often classified into several qualitative zones, based on subjective assessments of pollution factors, namely Rural, Urban, Industrial, and Marine atmosphere [1-6]. Generally, therural area is low corrosivity while Urban, Industrial, and Marine atmosphere are, respectively, higher corrosivity due to the existence of higher chemical contain in the atmosphere [3,4]. The corrosive of marine area relates to the existence of high Cl- concentrations in the atmosphere. Other chemical species that can be found in the Urban and Industrial atmospheres are SO2, CO2,and NO2, that product by gas emission from the combustion engine [6-8]. Further oxidation of SO2, usually in the presence of a catalyst such as NO2, forms H2SO4, and thus, acid rain could initiate [8]. Atmospheric corrosion, depends mainly on air pollution, is commonly initiates and develops under the thin water films, the film which is considered as surface electrolyte layer, formed by fog, dew, or raindrop. For a given time of wetness (time during which the wet film exists), the greater the pollution value, the greater the corrosivity formation. To know and elucidate the effect of the pollution on the corrosion behaviors, it is necessary to identify the pollutant substances, and likewise, the time of wetness should be taken into account. In this research, the corrosion behaviors of carbon steel affected by several types of ionic species were investigated by simulating artificial rainfall test. Three type of ACM sensors were used to create the empirical data for estimating the relation between sensor outputs and CRs. The chemical species and its concentration in the rainfall solution were taken as the main parameters of corrosion. 2. EXPERIMENTAL PROCEDURE 2.1 Chemical Composition in Rainfall Solution Chemical properties, pH values, and electrical conductivities of actual rain at National Institute for Material Science
  • 2. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 _______________________________________________________________________________________________ Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 383 (NIMS), Tsukuba, Japan, were analyzed. The measurement results show that the highest chemical concentration is HCO3 - and follow by NO3 -, SO4 - , and Cl- (as seen in Table (1)). The pH value and electrical conductivities are about 4.8 ~5.7 and 10~43 µs/cm respectively. In general, SO4 - , Cl-, and NO3 - are the most aggressive ionic species for corrosion acceleration [1, 2]. In this experiment, NaCl, KCl, Na2SO4, NaNO3, and KNO3 species, which are the major contain in the actual rain, were mixed with Deionized water and used as artificial rainfall solution. 2.2 Artificial Rainfall Equipment The artificial rainfall equipment, as seen in Fig. 1, composed of a chamber, a water reservoir, an air-compressor-mixer, ACM sensors which are connected to a Data logger, and a nozzle spray which is installed on the top of the chamber. The rainfall distribution is considerably uniform, and it can be adjusted to get a wide range of rainfall rate: 0.5 mm/h to 10 mm/h. However, the results of this experiment show that the rainfall rate, H (mm/h), is insensitive to the CRs and ACM sensors outputs. Hence, H= 1 mm/h was used for all cases. Table-1: Chemical properties in actual rainwater [9] Date 06-Jun 07-Jul 25-Jul Beginning Main pH (24 C) 5.5 4.8 5.2 5.7 Conductivity (µs/cm) 10 26 43 11 Concentration (mg/L) Cl- 0.7 0.6 2.4 0.7 SO4 2- 2.0 3.7 5.3 1.3 NO3 - 1.2 3.5 7.5 1.4 Na+ 0.3 0.5 2.0 0.4 K+ 0.3 0.7 2.3 0.7 Ca2+ <0.1 0.2 0.2 <0.1 Mg2+ <0.1 <0.1 <0.1 <0.1 HCO3 - <5.0 <5.0 <5.0 <5.0 (a) 3D representation (b) Schematic illustration Fig-1: Artificial rainfall equipment 2.3 Atmospheric Corrosion Monitoring (ACM) Sensor It has been known that galvanic couple sensing probe was used for dew detector [10] time-of-wetness meter [11], or moisture sensor [12]. Further integrations and applications of this type of sensor, which is called Atmospheric Corrosion Monitoring (ACM) sensor, has been used to predict the behaviors of corrosion under atmospheric condition [13]. The schematic illustration of ACM sensor, which consists of the Fe-Ag couple, is presented in the Fig. 2. The signal output, which can be called galvanic current, range between nanoampere to milliampere, depends mainly on the electrical conductivity of aqueous film formed by dew or raindrop on the striped surface of the sensor, as seen in Fig. 2 (b). And the signal outputs of the sensors are recorded and collected every minute by 16 CH Data logger SYRINX SAXM-50F. In this research, three types ACM sensors, Fe-Ag, Zn-Ag, and Al-Ag, were used to investigate the phenomenon of corrosion through the signal output of ACM censors. 2.4 Exposure Test and Measurement Low-carbon steel sheets, SPCC, were used as specimens and exposed to the artificial rainfall by a limited and single face. The backside, cut edge, and fringe of the specimens were covered by polyethylene sheetin order to avoid undesired corrosion occurs, as seen in Fig. 3. The ACM sensors and specimens were installed at the bottom of the chamber and incline 45o with a vertical plan. Each test was conducted 16 hours with two times repeated. The CRs were computed based on weight loss method; the samples were immersed in the Hydrochloric Acid (HCl) to remove the corrosion products or rust layer, then weight-loss was measured (ISO/DIS 8403.3 [14]). Fig-2: Schematic illustration of Fe-Ag ACM sensor, (a) overall view, (b) section view [13]. Aqueous
  • 3. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 _______________________________________________________________________________________________ Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 384 Fig-3: Carbon steel sheet specimens, (a) Preparation the specimen before exposure test, (b) After removing corrosion product. 3. RESULTS 3.1 Molarity and Electrical Conductivity The electric conductivity, σ (µs/cm), of all solutions linearly increase with the increasing of molarity, c (mol/L), (Fig. 4). In addition, Na2SO4 solutions present the highest electrical conductivity while NaCl and NaNO3 solutions are considerably similar trend line. It should be noted that the relation between σ and c follow a general formula: σ = β.c+ D (1) Where β is the electricity coefficient and D is electrical conductivity of deionize-water, in this experiment D ≈ 0.9 to 1.5 µs/cm. Fig-4: The eclectically conductivity of Na2SO4, NaCl, and NaNO3 solutions in function of molar concentration 3.2 Corrosion Rate Calculation After removing corrosion product, or rust layer, from the surface of the samples, weight loss was measured and converted to thickness loss. The thickness loss per year is called Corrosion Rate, CR (mm/y). The CR of the exposure sample can be calculated according to the following equation: CR(mm/y) = 10 Wy ρA (2) Where Wy is weight loss per year (g/y), ρ is the density of carbon steel (7.86g/cm3), and A is the exposed area (12.7×5.5cm2). 3.3 Effect of Rainfall Rate The rainfall rates were insensitive to CRs and ACM sensors outputs as seen in Fig. 5. It can be explained by the fact that the CR can approach maximum when the electrolytesurface film covering the metal become very thin, below 56 µm [1,9,15-17]. For the larger thickness of the film, especially under the rainfall with homogenous concentration, the CRs will stabilize at a constant value. Fig -5: The effect of rainfall rate to the sensor output in Na2SO4 solution with the concentration of 3×10-4 mol/L 3.4 Effect of Anions on Corrosion Rate In water, NaCl for instance, the molecules will separate into ions: Na+ (cation), and Cl- (anion). And likewise for KCl, NaNO3, and KNO3: K+, Cl-, Na+, NO3 -. The negative charge, called anion, is the most corrosive ion because it has much more tendency to catch electron from the metal surface. Consequently, the metal will oxidize by transferring the electron to the anion and liberating metal ion from metal the surface. Fig. 6 show CRs resulting from the effect of the anion and the variation of molarity. Evidently, Fig. 6 (a) and (b)indicate corrosion tendency depend on Cl- and NO3 - respectively, while the effect of K+ and Na+ is negligible. This Phenomenondoes not mean for all cation, especially H+ that has natural tendency to accept the electron from metallic-solution interface. (a) σ = 187791c +0.9 σ = 115047c + 0.9 σ = 108788c + 0.9 1.E+0 1.E+1 1.E+2 1.E+3 1.E+4 1.E-5 1.E-4 1.E-3 1.E-2 1.E-1 σ(µs/cm) Molarity, c (mol/L) Na2SO4 NaCl NaNO3 1.E-1 1.E+0 1.E+1 1.E+2 1.E+3 0 2 4 6 8 10 Sensoroutput,I(µA) Rainfall rate, H (mm/h) Fe-Ag Zn-Ag Al-Ag 0.01 0.1 1 10 1.E-5 1.E-4 1.E-3 1.E-2 1.E-1 CR(mm/y) Molarity, c (mol/L) KCl NaCl CR = 0.5 ±0.1 mm/y
  • 4. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 _______________________________________________________________________________________________ Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 385 (b) Fig-6: Effect of anion on corrosion rate, (a) the effect of Cl- ,(b) the effect of NO3 - 3.5 Relation between Corrosion Rate and Molarity Fig. 7 shows the logarithmic scale representation of CR in function of molar concentration. Each data point is the CR mean value of two-time repeated tests with three samples. As it can be seen, SO4 2- is the most aggressiveness anion, and follow by Cl- and NO3 -, respectively. According to the empirical data, the CR of Na2SO4 and NaCl indicate the transition from corrosion acceleration to deceleration and tend to reach a steady state when molarity is continuously increased. In particular, the CR of NaNO3 is considerably constant, CR ≈ 0.05 mm/y, for c < 3.10-3 mol/L, elsewhere, c > 3.10-3, the CR rapidly raises up. For the smaller concentration, c <3.10-5mol/L, all the CRs are approximately similar and remain steady. Fig-7: Corrosivity of carbon steel sheet corroded by Na2SO4, NaCl, and NaNO3 solutions 3.6 Relation between Sensor Outputs and Molar Concentration Fig. 8 shows the relation between sensor outputs in function of molar concentrations. The galvanic currents of the three sensors increase with the increasing of molar concentrations, except Al-Ag galvanic current in NaNO3 solution (see Fig 8 (c)) that considerably unchangeable when c> 10-4 mol/L. For Fe-Ag and Zn-Ag sensor, the galvanic currents in the Na2SO4 solutions are higher than those in NaCl and NaNO3 solutions, respectively (see Fig. 8 (a) and (b)). On the contrary, the Al-Ag galvanic currents in Na2SO4 solutions are lower than those in NaNO3 and NaCl solution (see Fig. 8 (c)). (a) (b) (c) Fig-8: Relation between molar concentration and sensor outputs, (a) Fe-Ag galvanic couple, (b) Zn-Ag Galvanic couple, and (c) Al-Ag galvanic couple. 0.01 0.1 1 1.E-5 1.E-4 1.E-3 1.E-2 1.E-1 CR(mm/y) Molarity, c (mol/L) NaNO3 KNO3 0.01 0.1 1 10 1.E-6 1.E-5 1.E-4 1.E-3 1.E-2 1.E-1 CR(mm/y) Molarity, c (mol/L) Na2SO4 NaCl Na2NO3 1.E-2 1.E-1 1.E+0 1.E+1 1.E+2 1.E+3 1.E+4 1.E-5 1.E-4 1.E-3 1.E-2 1.E-1 I(µA) c (mol/L) Na2SO4 NaCl NaNO3 0.1 1 10 100 1000 1.E-5 1.E-4 1.E-3 1.E-2 1.E-1 I(µA) Molarirty, c (mol/L) Na2SO4 NaCl NaNO3 1.E-1 1.E+0 1.E+1 1.E+2 1.E+3 1.E+4 1.E-5 1.E-4 1.E-3 1.E-2 1.E-1 I(µA) Molarity, c (mol/L) Na2SO4 NaCl NaNO3 Deionized water
  • 5. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 _______________________________________________________________________________________________ Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 386 3.7 Relation between CR and Sensor Output Recall that; the sensor output is a current of the galvanic couple that highly depend on ionic species in the aqueous film formed on the surface of ACM sensor. Fig. 9 (a), (b), and (c) present the outputs of the three sensors, Fe-Ag, Zn- Ag, and Al-Ag in function of CR. With Na2SO4, NaCl, and NaNO3 solutions, the sensor outputs of Fe-Ag and Zn-Ag couple are relatively similar and congregated as a curve, as seen in Fig. 9 (a) and (b). Conversely, the outputs of Al-Ag sensor are completely deviated by chemical species (Fig. 9 (c)). Additionally, Na2SO4solution is less sensitive to the Al- Ag sensor output, while it is sensible to the Fe-Ag and Zn- Ag. (a) (b) (c) Fig -9: Relation between sensor output and CR, (a) Fe-Ag, (b) Zn-Ag, and (c) Al-Ag galvanic couple 4. DISCUSSION Atmospheric corrosion is an electrochemical process which can only proceed in the presence of an electrolyte film. It is, therefore, to be considered as discontinuous process, where the total corrosion loss, COR, in a given time or period is determined by the time of wetness, twn, and the average of corrosion rate, CR, during the each period, n, of condensation[1]: COR = ∑ twn . CRnn (3) The calculation the time of wetness based on meteorological data (by taking RH≥ 80% and T ≥ 0 0C) might not achieve the exact time that makes corrosion possible. Thus, the technical measurement method using ACM sensor exposure to the actual environment is more preferable. Virtually, Fe- Ag and/or Zn-Ag galvanic couples enable to estimate the time of wetness, twn, and corrosion rate,CRn, through the empirical data (see Fig. 9 (a) and (b)). Al-Ag couple, however, is unable to forecast the CR in the unknown pollution species, especially the mixed species in the atmosphere, due to the inconsistent relation of I-CR in different solutions (Fig 9 (c)). Nonetheless, the Al-Ag enables to estimate the time of wetness based on the great lifetime service. And also, it allowspredicting the chemical species in the environment. For instance, if the CR is high, and the Al-Ag sensor output is low, the SO4 2- ions is assumed as the major contain in the solution or the environment. It has to be noted that the service-life of Fe-Ag galvanic sensor is much lower than those of Zn-Ag and Al- Ag, respectively. The rust layer could be visually detected on the striped surface of the Fe-Ag sensor after about 64 hours rain (see Fig. 10), and it results to the increasing of the sensor output and decreasing the sensibility of the sensor. Thus, it is recommended to change the sensor frequently during the exposure test. 5. CONCLUSION The experimental analysis of the corrosion behaviors under the artificial rainfall investigation allows to conclude as below: - The rainfall rates were insensitive to ACM sensors outputs and CRs. In contrast, the chemical species and their concentrations in the rainfall solution significantly affected the ACM outputs and the CRs. - The corrosivity ofcations is negligible compared to anions. For a certain of molar concentration, the most aggressiveness ions are SO4 -, Cl-, and NO3, respectively. - For further increasing molar concentration, the CR tends to reach a steady state at the maximum value of CR = 2mm/y. - The ACM sensors are capable of estimating the time of wetness and aggressivity of atmosphere, and thus the total corrosion loss could be estimated. - The lifetime of Fe-Ag galvanic sensor is much shorter than those of Zn-Ag, and Al-Ag respectively since the rust layer visually appears after 64 hours rain; thus the sensibility of the sensor would not performwell. 1.E-2 1.E-1 1.E+0 1.E+1 1.E+2 1.E+3 1.E+4 0.01 0.1 1 10 I(µA) CR (mm/y) Na2SO4 NaCl NaNO3 1.E-1 1.E+0 1.E+1 1.E+2 1.E+3 0.01 0.1 1 10 I(µA) CR (mm/y) Na2SO4 NaCl NaNO3 1.E-1 1.E+0 1.E+1 1.E+2 1.E+3 1.E+4 0.01 0.1 1 10 I(µA) CR (mm/y) Na2SO4 NaCl NaNO3
  • 6. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 _______________________________________________________________________________________________ Volume: 05 Issue: 08 | Aug-2016, Available @ http://ijret.esatjournals.org 387 Fig-10: Overview of corroded sample after 16 hours rain with NaCl 10-2 mol/L, and ACM sensor after 80 hours rain REFERENCES [1] F. Mansfeld: Applied Sciences, 203(Electrochemical and Optical Techniques for the Study and Monitoring of Metallic Corrosion, 1991) pp. 571-584. [2] ISO 9223: Corrosion of metals and alloys, Corrosivity of Atmospheres. Classification, (1992). [3] D. de la Fuente, I. Díaz: Corrosion Science. 53 (2011) pp. 604–617 [4] M. Morcillo B. Chico: Corrosion Science. 77 (2013) pp. 6–24 [5] Sei J. Oha, D.C. Cookb: Corrosion Science 41 (1999) pp. 1687-1702 [6] J. Morales, S. Martin-Krijerz: Corrosion Science 47 (2005) pp. 2005–2019 [7] S. Sudalma, P. Purwanto: Procedia Environmental Sciences 23 ( 2015 ) pp. 247 – 252 [8] Jekti Prihatin, A. Duran Corebima, Ariffin, Abdul Gofur, The effect of exposure of mulberry to acid rain on the defects Cocoon of Bombyxmori L, Procedia Environmental science 23 (2015) 186-191 [9] T. Shinohara: ISSN 0892-4228, Corrosion Engineering, 63 (2014) pp. 86-92. [10] P.J. Sereda: ASTM Bulletin, No. 228, (1958) pp. 53: ibid., No.238. (1958) pp. 61; ibid., No. 246, (1960) pp. 47 [11] P.R. Grossman: “Atmospheric Factors Affecting Corrosion of Metals,“ Ed. By S.K Conburn, p. 5, ASTM STP 66 (1978). [12] P.J. Sereda, S.G. Croll and H.F. Slade: “Atmospheric Corrosion of Metal,” Ed. By S.W. Dean, Jr. and E.C Rhea, p. 267, ASTM STP 767 (1982). [13] S.i. Motoda, Y. Suzuki, T. Shinohara: Corrosion Engineering. 43 (1994) pp. 583-594. [14] ISO/DIS 8403.3: Metals and alloys. Procedures for removal of corrosion products from corrosion test specimens, 1985. [15] M. Stratmann, H. Strecke: Corrosion Science. 30 (1990) pp. 715–734. [16] A. Nishikata, Y. Ichihara: J. Electrochem. Soc. 144 (1997) pp. 1244–1252. [17] T. Tsuru, A. Nishikata: Mater. Sci. Technol. A198 (1995) 161–168. Fe-Ag Zn-Ag Al-Ag Corroded samples 16h rain Rust layer