justnes-corrosion inhibitors for concrete
TRANSCRIPT
Civil and Environmental Engineering
Corrosion inhibitors for concrete
Prof. Harald JustnesSINTEF Concrete
NO-7465 Trondheim, Norway
Civil and Environmental Engineering
Content
Introduction to corrosion and inhibitors Short review of some recent literature. Calcium nitrate is shown to be an inhibitor against chloride
induced corrosion of rebars in concrete, similar to the well-known calcium nitrite.
Demonstrated by pictures of rebars in concrete exposed for chlorides and theory after LPR experiments on mild steel inserts in mortar.
Presentation of extended research program for laboratory and field comparison of calcium nitrate and nitrite performance as inhibitors.
Civil and Environmental Engineering
Bridge over troubled waters….
Chloride induced corrosion of rebars is perhaps the most common degradation mechanism world wide.
This bridge had to be rebuilt due to heavy corrosion after 25 years
Civil and Environmental Engineering
Close-up of concrete element of bridge
Severe situation since the pre-stressed cables also were corroded. The bridge was demolished and a new one built Could inhibitors have prevented this situation?
Civil and Environmental Engineering
Definition of corrosion inhibitor
A corrosion inhibitor is defined as a compound that delays the initiation or propagation of corrosion.
An inhibitor does not prohibit corrosion from occurring.
Some people like to use the term “corrosion retarder” instead.
Civil and Environmental Engineering
Corrosion of rebar
Oxygen reduction to hydroxyl ions at cathode; O2 + 2 H2O +4 e- = 4 OH-
Iron oxidized first to ferrous hydroxide at the anode; Fe(s) + 2 OH- = Fe(OH)2 + 2 e-
Fe(OH)2 can diffuse away as complex ion, Fe(OH)4-xClx2- and oxidize 4 Fe(OH)2 + O2 + 2 H2O = 4 Fe(OH)3
Ferric hydroxide has 2-4x higher volume than the metal cracking
Civil and Environmental Engineering
Cathodic and anodic inhibitors
Cathodic inhibitors delays the reduction of oxygen by complex formation at the surface of iron/iron oxide; Aminoalcohols like DMEA; (CH3)2N-CH2CH2OH ”Organic” corrosion inhibitors (OCI) as blend of aminoalcohol
(active) and ester emulsion (passive) ”Migrating” corrosion inhibitors (MCI) as substituted ammonium
benzoates (liberates amine by alkalis in situe)
Anodic inhibitors oxidizes ferrous hydroxide to ferric hydroxide at the steel and strengthen passive layer; Inorganic salts of nitrites, NO2
-, e.g. Ca(NO2)2 Inorganic salts of nitrates, NO3
-, e.g. Ca(NO3)2
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3 potential applications of inhibitors
1. In patch work repair
2. Applied on the surface for migration to the rebar (MCI)
3. In the bulk concrete from construction
The latter method seems to function best according to literature data.
Civil and Environmental Engineering
Long-term effect of inhibitors in patchwork repairNACE Corrosion 2003, San Diego, March 19, paper 03286by Ali Akbar Sohanghpurwala, Concorr inc.
Tested calcium nitrite and 2 different amines (MCI). Evaluations 2, 5 and 6 years after repair. 3 constructions with sufficient chloride to initiate corrosion
showed that corrosion initiated and propagated in spite of the presence of inhibitors.
No difference relative to reference was observed.
Civil and Environmental Engineering
Corrosion Inhibitors in Concrete-1
NACE Corrosion 2003, San Diego, March 19, paper 03288by R.J. Kessler, R.G. Powers & W.D. Cerlanek
Tested calcium nitrite, ORG1 and ORG2 Exposed in 3% NaCl in outdoor tank after 90 days curing Conclusion:
Calcium nitrite was the only inhibitor to show significant increase in TCI and TTF in non-pozzolanic concrete (w/c = 0.41)
20% FA lead to >3x TCI and TTF relative to control 8% SF lead to >6x TCI and TTF relative to control
TCI = time to corrosion initiationTFF = time to failure
Civil and Environmental Engineering
Corrosion Inhibitors in Concrete-2
Admixture TCI, -280 mVvs SCE (days)
TTF (days) % failed
None 209 298 100
ORG1 245 418 100
DCI-S 484 571 100
ORG2 168 279 100
20% FA >757 >958 80
8% SF >1793 >1793 0
Civil and Environmental Engineering
Accelerated testing of inhibitors
Kondratova, Montes & Bremner, ACI SP192-48, 2000
Concrete with w/c = 0.25, 0.40 or 0.60, 20 mm cover,0.4 mm crack or not, 3 inhibitors; CNI, OCI and MCI.
Exposed to artificial seawater in lab. Using LPR++ Conclusion:
CNI effective in sound and cracked concrete of w/c = 0.40 - 0.60. OCI effective in sound and cracked concrete of w/c = 0.40, but
only in sound concrete at w/c = 0.60 MCI was effective in sound concrete of w/c 0.60 and increased
corrosion rate in crack and also for w/c = 0.40 without crack. Pitting corrosion in cracks for HPC (w/c = 0.25), which seems to be
deeper when inhibitors were present.
Civil and Environmental Engineering
Natural marine exposure of concrete
Kondratova, Montes & Bremner, Cement and Concrete Composites, Vol. 25, 2003, p. 483-490
2 inhibitors; CNI (calcium nitrite) and OCI (amine based) w/c = 0.40, 505 kg cement/m3, sound and pre-cracked Treat Island in Bay of Fundy, Maine, 120 freeze/thaw yr Conclusions:
Beneficial with inhibitors in sound concrete In pre-cracked concrete with 20 mm cover, significant localised
corrosion at 1 yr and cracking due to corrosion after 3 yrs 5 OCI more efficient than 25 CNI/m3 uncracked concrete In pre-cracked concrete (0.2 and 0.4 mm), both OCI and CNI was
relatively inefficient
Civil and Environmental Engineering
Rebars cast in concrete (SINTEF)
20 mm rebars were cast in the center of concrete cylinders of 100 mm diameter and 200 mm height, leading to a concrete cover of 40 mm
The concrete consisted of ordinary Portland cement (CEM I-42,5-R), natural sand, crushed gravel and tap water to w/c = 0.54.
The concrete was added 0, 2 or 4 % dry calcium nitrate (CNA), Ca(NO3)2, of cement weight.
Civil and Environmental Engineering
Chloride exposure Series 1: Intermixed chlorides in the form of 3.2 %
NaCl of cement weight dissolved in water.
Series2: Intruded chlorides after 56 days moist curing by exposure to cyclic drying and wetting by 5% NaCl.
Series 1&2 stored at 38°C and 90% RH with air access and inspected for cracks every 3 months.
3 specimens were made for each of 6 variants.
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Reference concrete after 2 years
38ºC, 90% RH storage Chlorides intruded by
drying/wetting cycles after 56 days curing
Upper photo rebar Lower photo imprint of
rebar
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Concrete with 2% CNA after 2 years
38ºC, 90% RH storage Chlorides intruded by
drying/wetting cycles after 56 days curing
Upper photo rebar Lower photo imprint of
rebar
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Concrete with 4% CNA after 2 years
38ºC, 90% RH storage Chlorides intruded by
drying/wetting cycles after 56 days curing
Upper photo rebar Lower photo imprint of
rebar
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3.2 % NaCl intermixed concrete stored 3 years at 90% RH & 38°C
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Concrete with 2% CNA & 3.2% NaCl intermixed after 3 years
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Concrete with 4% CNA & 3.2% NaCl intermixed after 3 years
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Steel from concrete with 3.2% NaCl intermixed after 3 years
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Steels from concrete with intruded chlorides after 4 years
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Corrosion of mild steel in mortarBase mortar composition:
1.00 parts OPC cement
3.00 parts standard sand
0.20 parts lime stone filler
0.55 parts tap water
Mortars made with both 0 % and 3.86 % CNA.
Civil and Environmental Engineering
Experiment mortars with steel
Proceeding the lime water curing for 55 days after 1 day in covered molds:
Mortars with embedded steel were stored at 50% R.H. for 7 days and immersed in 5% NaCl solution for 3 days
The procedure was repeated twice (totally 3) in order to create a high Cl- concentration that would initiate corrosion
The prisms were stored at 90% R.H. until the corrosion rate measurements
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Polarization resistance measurements
Corrosion rate evaluated by average corrosion current; icorr < 0.1- 0.2 A/cm2 = negligible corrosion icorr > 0.2 A/cm2 = active corrosion icorr > 1 A/cm2 = important corrosion icorr > 10 A/cm2 = severe corrosion
33Ø6
40
160
40
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Corrosion current
After a total of 14 months curing:
without CNA
icorr = 2.8 ± 0.8 A/cm2= important corrosion
(High S.D. due to 1 parallel low; 3.2, 3.2 and 1.9)
with 3.86 % CNA
icorr = 0.54 ± 0.05 A/cm2= active corrosion
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Corrosion current
After a total of 25 months curing:
without CNA
icorr = 8 ± 5 A/cm2 = important severe corr.
(High S.D. due to 1 parallel low; 11.7, 10.6, 2.6)
with 3.86 % CNA
icorr = 0.29 ± 0.07 A/cm2= active negligible
Chloride content in mortars determined to 2.5 % Cl- of the cement weight
Civil and Environmental Engineering
Conclusion corrosion rate
Effect of 3.86 % CNA addition on Cl- induced average corrosion rate:
Reduced with a factor of 5after 14 months curing
Reduced with a factor of at least 26after 25 months curing
Is nitrate (NO3-) as good a corrosion
inhibitor as nitrite (NO2-)?
Civil and Environmental Engineering
Nitrite inhibiting mechanism Sacrificial reduction of nitrite to form FeOOH (or
similar) at the anode, which will stifle iron dissolution:
Red.: NO2- + H2O + e- = NO + 2 OH- E0 = - 0.46 V
Ox.: Fe(OH)2 (s) + OH- = Fe(OH)3 (s) + e- E0 = + 0.56 V
which combine to the total reaction;
Fe(OH)2 (s) + NO2- + H2O =
Fe(OH)3 (s) + NO + OH- E0 = + 0.10 V
Civil and Environmental Engineering
Nitrate inhibiting mechanism Nitrate will give an extra reduction step
compared to nitrite;
2 Fe(OH)2 (s) + NO3- + H2O = 2 Fe(OH)3 (s) + NO2
-
E0 = + 0.57 V
This imply that nitrate, NO3- , should be an even
better inhibitor than nitrite, NO2- , since two more
moles of ferrous iron are oxidized to ferric per mole nitrogen oxide added!
Civil and Environmental Engineering
Nitrates is less harmful than nitrites
Impure form of calcium nitrate (with some ammonium) is actually used as fertilizers and spread in the fields.
Acute lethal dosage for 50% rats by oral route (LD50) is for Sodium nitrite, NaNO2, 180 mg/kg Sodium nitrate, NaNO3, 1,267 mg/kg Calcium nitrate tetrahydrate, Ca(NO3)·4H2O, 3,900 mg/kg
In addition nitrites are mutagenic and nitrates not.
Civil and Environmental Engineering
Extended program nitrate vs nitrite-1 Extended program initiated autumn 2001
Concrete recipe 350 kg OPC/m3, w/c = 0.47
14 concrete mixes for rebars in cylinders in lab/field:
2 types commercial calcium nitrate, commercial calcium nitrite and sodium nitrite
2 dosages calcium nitrate, one dosage others + reference
Mixes with intruded and intermixed (3.2%) sodium chloride
Civil and Environmental Engineering
Reference with intermixed chlorides after ~3 years at the roof top (average T = 5C)
Cracked
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Rebar of concrete with intermixed chloride
3 years weather exposure of reinforced concrete on roof top. ”Green rust” to the left as ferrous hydroxy-chloro complex in newly opened
specimen with intermixed chlorides (Fe2+ sign of limited O2) After the rebar has been laying 3 days in laboratory air, the ”green rust” had
turned into ordinary red ferric rust by oxidation (Fe2+Fe3+)
Civil and Environmental Engineering
Extended program nitrate vs nitrite-2
3 self compacting concrete (w/c = 0.50) reinforced wall elements were cast, instrumented and placed (3 days old) in the tidal zone + “lollipops” for rapid test.
The three mixes were reference (no admixture), 4% calcium nitrate by cement weight and equivalent commercial calcium nitrite (i.e. equal amount molar nitrite as nitrate in mix 2).
Civil and Environmental Engineering
“Lollipop” test-1 Concrete recipe w/c = 0.50 with 330 kg OPC Reference (0% admixture) 4% dry calcium nitrate bwoc Equivalent molar dosage of commercial calcium nitrite 100x280 mm cylinders were cast with 20 mm rebar in the
center and 50 mm from bottom, leaving cover of 40 mm. Test is an impressed current test (5V DC) measures time
to failure. Increase in current flow and eventually cracking due to expanding corrosion products.
Brown, R.P. and Kessler, R.J. in Report no. 206, Florida Dept. Transportation Office of Materials and Research. October 1978.
Civil and Environmental Engineering
“Lollipop” test- 2 concrete propertiesProperty Reference Nitrate NitriteFreshSlump (mm)Density (kg/m3)Air (vol%)
14024252.1
16023953.1
13524202.3
c, 1 d (MPa) 28.90.1 21.10.2 25.90.6c, 28 d (MPa) 54.50.6 60.30.6 77.30.590 daysc, 90 d (MPa) (kg/m3)dry (kg/m3)cap (vol%)mak (vol%)
66.10.92691423892610.10.71.20.2
70.50.42690523671210.50.31.50.06
84.01.3268842394129.90.31.00.03
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“Lollipop” test - 3 Set-up
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“Lollipop” test - 4 Example
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“Lollipop” test - 5 Experiment
Reference; 32 days to current increase, 2 of 3 cracked at 37 days Nitrite; 32 days to current increase, 2 of 3 rust up along rebar at 33 d Nitrate; small crack at 65 days. Corrosion products seen at 120 days
5 V "Lollipop" testing of rebar corrosion
10,012,014,016,018,020,022,024,0
0 20 40 60 80 100 120Time (days)
Cur
rent
(mA
) pa
ssin
g
ReferenceNitrateNitrite
Civil and Environmental Engineering
Wall element concreteProperties Ref. Nitrate NitriteFresh mix
Density (kg/m3)Air (vol%)
2,3845.2
2,3444.8
2,3803.0
1 dayc (MPa) 22.10.2 19.00.3 24.40.3
7 daysc (MPa) 45.30.1 47.80.6 61.90.4
Daysc (MPa)
3556.90.7
3458.30.5
2873.50.6
1 yearc (MPa) (kg/m3)C0, Cl (%)
DCl (10-12m2/s)r (m)
65.20.324125
0.890.077.81.0731
65.51.023972
0.960.019.91.3702
85.42.424572
0.990.076.40.5692
Civil and Environmental Engineering
Instrumented reinforcement element
2 types electrodes in 3 level (bottom, middle, top), a special sensor for detection of intruded chlorides, 3 bends for stress corrosion cracking. 2 reinforcement nets with 20 and 50 mm concrete cover.
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Special sensor for chloride intrusion
As chlorides intrudes, corrosion will start first on the rebar closest to the surface. By measuring of potential difference between thick, rear rebar parallel to surface against thinner, perpendicular rebars at different depths, an indication of how deep chlorides have penetrated at a given time can be obtained.
Civil and Environmental Engineering
Placing instrumented, reinforced concrete wall elements in tidal zone
2 of 3 walls (light grey) at Østmarkneset at low tide. Walls are identical but cast without inhibitor, with 4% calcium nitrate and with equivalent dosage of commercial calcium nitrite, respectively.
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Preparing to measure
Wires from all electrodes etc is collected in a box at the top of the wall element to enable quick measurement of all electrodes with a simple multimeter at low tide.
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Reinforcement grid with 20 mm cover
Average of 3 electrodes at different levels from bottom
ERE20 average potentials 10-12 vs 16
0
60
120
180
240
300
360
1 10 100 1000Time (days)
Pote
ntia
ls (m
V)
Ref
Nitrate
Nitrite
Civil and Environmental Engineering
Reinforcement grid with 50 mm cover
Average of 3 electrodes at different levels from bottom
ERE20 average potentials 10-12 vs 17
-40
20
80
140
200
260
320
380
1 10 100 1000Time (days)
Pote
ntia
ls (m
V)
RefNitrateNitrite
Civil and Environmental Engineering
Conclusion-1
Anodic inhibitors seems to function better than cathodic according to literature review.
Calcium nitrate is an anodic inhibitor against chloride induced corrosion of steel in concrete.
It works both for intruded and intermixed chlorides.
3-4% dry calcium nitrate of cement weight seems to be sufficient to obtain good protection of the rebar
Civil and Environmental Engineering
Conclusion - 2 The inhibitor mechanism of nitrate (NO3
-) is analogous to the well-known corrosion inhibitor nitrite (NO2
-), but the kinetics may be slower.
According to mechanism, calcium nitrate provides a higher buffer as corrosion inhibitor than calcium nitrite at equimolar dosage.
Calcium nitrate is less harmful, available in larger amounts and cheaper than calcium nitrite.
Civil and Environmental Engineering
SINTEF not the only one to claim that nitrate work as inhibitor
Al-Amoudi et al. Cement and Concrete Composites, Vol. 25, May 2003, pp. 439-449
Concrete with w/c = 0.45 and 350 kg c/m3
Exposed to chloride, chloride/sulphate, seawater, brackish water, unwashed aggregate
2 and 4% calcium nitrite by weight of cement 2, 3 and 4% calcium nitrate by weight of cement CI1 inhibitor (organic) in recommended dosage (5 /m3) CI2 inhibitor (organic) in recommended dosage (1.2 kg/m3) Current density by LPR method reported.
Civil and Environmental Engineering
Current densities (A/cm2) after 122 days,Al-Amoudi et al
Nitrite NitrateCont. Ref2% 4% 2% 3% 4%
CI1 CI2
Cl-Cl-/SO4
2-
SeaBrackishNo wash
.52
.55
.54
.28
.24
.06
.10
.04
.03
.08
.06
.06
.04
.03
.06
.06
.07
.06
.06
.06
.06
.06
.06
.06
.06
.06
.07
.06
.05
.06
.07
.08
.09
.05
.11
.08
.08
.11
.12
.14.06