Construction and Building Materials: Ali Mardani-Aghabaglou, Gözde - Inan Sezer, Kambiz Ramyar
Construction and Building Materials: Ali Mardani-Aghabaglou, Gözde - Inan Sezer, Kambiz Ramyar
Construction and Building Materials: Ali Mardani-Aghabaglou, Gözde - Inan Sezer, Kambiz Ramyar
h i g h l i g h t s
The contribution of silica fume and metakaolin to the strength was started as early as 3 days.
For the y ash this duration was 180 days.
Mineral admixtures improved transport properties greater than mechanical properties.
The presence of the mineral admixture and its type changed the ettringite morphology.
a r t i c l e
i n f o
Article history:
Received 1 May 2014
Received in revised form 13 June 2014
Accepted 23 July 2014
Available online 15 August 2014
Keywords:
Mineral admixture
Microstructure
Transport properties
Durability performance
a b s t r a c t
In this study the effect of cement replacement with y ash, silica fume and metakaolin on the compressive strength, dynamic elastic modulus, chloride-ion penetration, water absorption, water sorptivity, and
freezethaw and sulfate resistance of the mortar mixtures were comparatively investigated. In addition,
micro-structural investigation was performed on some selected mortar mixtures, and regression analysis
was applied on the sulfate resistance test results. It was observed that, the presence of the mineral admixture and its type changed the ettringite morphology. Besides, only ball-ettringite and a special type of
ettringite were observed in the silica fume- and metakaolin-bearing mixtures, respectively. The needle-like and ball-ettringite formation were found in the y ash mixtures. In the control mixture the needle-like, ball-ettringite and massive ettringite were detected. Overall test results revealed that the
performance of the mixtures was arranged in descending order as silica fume-, metakaolin-, y ash-bearing mixtures and the control one.
2014 Elsevier Ltd. All rights reserved.
1. Introduction
Some of the mineral admixtures used nowadays are industrial
by-products [1,2]. Silica fume is a by-product of the manufacture
of silicon metal and ferrosilicon alloy and it contains more than
8085% SiO2 in amorphous form. Thus, it has highly pozzolanic
properties and is suitable to use in the cement and concrete industries [36]. Metakaolin is produced by calcinations of pure or
rened kaolinitic clay at a temperature range between 650 and
850 C. It is also a processed amorphous silica material [7]. Fly
ash is obtained as a waste product upon the combustion of pulverized coal in thermal power plants [810].
Mineral admixtures are used as cement replacement material in
mortar mixtures and several special types of concrete such as selfcompacting, reactive-powder, roller compacted and lightweight
concrete. Mineral admixtures are used in order to improve
Corresponding author. Tel.: +90 232 3886026; fax: +90 232 3425629.
E-mail address: ali.mardani16@gmail.com (A. Mardani-Aghabaglou).
http://dx.doi.org/10.1016/j.conbuildmat.2014.07.089
0950-0618/ 2014 Elsevier Ltd. All rights reserved.
18
dynamic elastic modulus, chloride ion penetration, water absorption, water sorptivity, sulfate resistance and freezethaw resistance of cement mortars. For this purpose, 10 w% of the cement
was replaced with y ash, silica fume and metakaolin. The 7, 28,
90, 180 and 300-day compressive strength, as well as 300-day
transport properties and freezethaw resistance of the mortar mixtures were determined. Besides, the behavior of the mixtures
exposed to sodium and magnesium sulfate solutions for 300 days
was studied. In addition micro-structural investigation and regression analysis was performed on mortar mixtures exposed to sulfate
attack.
2. Experimental study
2.1. Materials
In this study, a CEM I 42.5 R type cement conforming to EN 197-1 standard [21]
was used. A high-lime (class C according to ASTM C 618-03 [22]) y ash conforming
to EN 450-1 standard [23], a silica fume and a metakaolin were used as the cementitious material. Pozzolanic activity indices of the mineral admixtures were determined according to ASTM C311 [24]. The chemical composition, as well as some
mechanical and physical properties of the cement, y ash, silica fume and metakaolin obtained from their manufacturers, is presented in Table 1. The standard sand
conforming to EN 196-1 standard [25] with saturated surface dry bulk specic gravity of 2.72 and absorption capacity of 0.70% was used.
In all of the mixtures, water/binder (w/b) ratio and sand/binder (s/b) ratio were
kept constant as 0.485 and 2.75 (by weight), respectively. In addition to the control
mixture containing no mineral admixture; in the test mixtures, 10 wt% of portland
cement was replaced with y ash, silica fume and metakaolin. Flow values of the
fresh mortar were determined in accordance with ASTM C1437 [26]. The recorded
ow values were in the range of 170 20 mm. The lowest ow values were
obtained in the mixtures containing either silica fume or metakaolin. This was
due to the extremely high neness values of these admixtures.
2.2. Test procedures
mt
Ad
Edn qc2
resistance of the mortar mixtures cured for 300 days in water were determined
in accordance with ASTM C1202 [30], ASTM C642-97 [31], ASTM C1585 [32] and
ASTM C 666 [33] standards, respectively.
For chloride penetration test, the amount of electrical current passed through
the cylinder specimens was measured for 6 h. At the end of 6 h the total charge
passed, in coulombs, was measured. For water absorption test, saturated surface
dry specimens were weighed and then kept in an oven at 105 5 C until attaining
a constant mass. For freezethaw resistance test, the mortar specimens were frozen
in air from 5 2 C to 18 2 C within 3 h and were thawed in 5 2 C water
within 1 h in a single cycle. The changes in weight of each specimen were calculated
at every 30 freezethaw cycles until 300 cycles in accordance with TSE CEN/TS
12390-9 [34] standard. For water sorptivity test, the specimens were dried at
105 C until a constant weight, and then the side surfaces of the specimens were
sealed with an acrylic copolymer-based sealing material. Supporting rods were
placed at the bottom of a pan and the pan was lled with the tap water to provide
13 mm water level on the top of the supporting rods. At 0, 5, 10, 20, 30, 60, 120,
180, 240, 300, 360 min time intervals the specimens were weighed. The sorptivity,
I, was obtained from Eq. (2):
1 m1 2m
1 m
where, Edn = dynamic elastic modulus of the mortar (MPa), q = hardened density
(kg/m3), c = ultrasonic pulse velocity (km/s) and m = Poissons ratio. Poissons ratio
was assumed as 0.2 for all of the mixtures.
The 100 50 mm cylinder specimens were prepared for chloride-ion penetration, water absorption and freezethaw resistance tests. In addition,
40 40 160 mm prism specimens were prepared for water sorptivity test. The
chloride-ion penetration, water absorption, water sorptivity and freezethaw
Table 1
Some physical, chemical and mechanical properties of using materials.
Chemical Composition (%)
Cement
FA
SiO2
23.84
32.80
Al2O3
4.2
13.77
Fe2O3
3.4
4.78
CaO
61.0
39.69
MgO
1.8
2.05
Na2O
0.20
0.40
K2O
0.46
1.18
SO3
2.93
4.22
Cl
0.0064
LOI
1.74
1.34
IR
0.30
SF
87.29
0.47
0.63
0.81
4.47
1.25
1.28
0.22
2.70
MK
63.53
32.36
0.54
0.29
0.18
0.33
1.08
0.01
1.00
25
37.2
44.6
Cement
Fly ash
Silica fume
Metakaolin
110
166
1
3.11
2.29
2.10
2.20
7-Day
69
101
102
3360
4040
18000
11768
28-Day
79
132
110
19
70
Control
10% Metakaolin
60
55
50
Control
45
40
10% Metakaolin
35
30
25
0
50
100
150
200
250
300
Age (Days)
65
50
40
30
20
10
0
28
90
180
300
7-Days
90-Days
300-Days
28-Days
180-Days
UPV (Km/s)
5
4
3
2
1
0
Control
10% FA
10% MK
10% SF
Control
70
65
60
55
50
45
40
35
30
25
3.8
y = 29.22x - 85.419
r = 0.9925
4.3
70
4.8
UPV (Km/s)
(a)
(b)
10% Metakaolin
65
60
55
y = 28.312x - 81.228
r = 09881
50
45
40
35
30
25
3.8
70
10% Fly Ash
65
60
55
y = 33.42x - 104.92
50
r = 0.9948
45
40
35
30
25
3.8
4
4.2 4.4 4.6
UPV (Km/s)
20
4.2
4.4
4.6
4.8
5.2
70
4.8
5.2
4.8
5.2
10 % Silica Fume
65
60
y = 32.565x - 101.35
r = 0.9951
55
50
45
40
35
30
25
3.8
UPV (Km/s)
4.2
4.4
4.6
UPV (Km/s)
(c)
(d)
Fig. 4. Relationship between compressive strength and UPV values of mortar mixtures: (a): control mixture, (b) 10% y ash, (c) 10% metakaolin, (d) 10% silica fume.
3000
3211
2500
2000
1500
1824
1000
1089
500
759
Control
10% FA
10% MK
10% SF
3500
(mm/s1/2)
1x10-3
4000
6
5
5.9
4.8
4
3
3.4
2.9
2
1
0
Control
CEP [37] : Water absorption ratio is
< 3% Good,
3-5% Average,
>5% Poor.
4
4.2
3
3.1
2.8
1.8
10% FA
10% MK
10% SF
inclusion of mineral admixture. The sorptivity values of the control, y ash-, metakaolin- and silica fume-bearing mixtures were
5.9, 4.8, 3.4 and 2.9 mm, respectively. Silica fume showed the most
superior result compared to the other pozzolans. The reason for
improvement of the transport properties of the mixtures are similar to those given for the strength and UPV test results.
Fig. 8 indicates that, there is a strong relationship between
water absorption and chloride ion penetration of the mortar
mixtures.
3.4. Sulfate resistance
Control
10% FA
10% MK
10% SF
3500
3000
2500
2000
1500
1000
500
0
1.5
2.5
3.5
4.5
the control mortar had the highest length change values at all ages
compared to those of the pozzolanic mortars. However, the difference between expansion values of the control and the pozzolanic
mixtures increased by increasing the pozzolanic activity index of
the mineral admixture incorporated to the mortar. The expansion
values of the mortar mixtures immersed in sodium sulfate solution
were lower than the expansion of these immersed in the magnesium
sulfate solution. The more destructive effect of magnesium sulfate
compared to that of sodium sulfate is attributed to the destruction
of CSH upon magnesium sulfate attack [1,2].
0.3
Control
10% Fly Ash
10% Metakaolin
10% Silica Fume
Expansion (%)
0.25
0.2
0.15
0.1
0.05
0
0
30
60
90
120
150
180
210
240
270
300
(a)
0.35
Control
10%Fly Ash
10% Metakaolin
10% Silica Fume
Expansion (%)
0.3
0.25
0.2
0.15
0.1
0.05
21
0
0
30
60
90
120
150
180
210
240
270
300
(b)
Fig. 9. Expansion values of mortars mixtures (a) Na2SO4 and (b) MgSO4.
A multiple regression analysis was applied to obtain the following relationship between sodium sulfate expansion, exposure period and pozzolanic activity index the of mineral admixture.
22
Silica fume
mixture
Metakaolin
mixture
Fly ash
mixture
Control
mixture
Control
Mixture
(Before
the
damage)
Control
mixture
(After
the
damage)
Fig. 10. Images of mortar mixture at the end of 300-day sulfate attack.
XX
X
Fig. 11. SEM images of the control mortar mixtures (E: Ettringite, G: Gypsum).
where, E: expansion values of the mortars in sodium sulfate solution (%), D: sodium sulfate solution exposure period (days) and P:
28-day pozzolanic activity index of the mineral admixture (%).
The estimated values are in a good agreement with the experimental values obtained in this study. The coefcient of correlation
between estimated and experimental values is 0.89. In the other
23
Fig. 12. SEM images of the y ash mortar mixtures (E: Ettringite, CH: calcium hydroxide).
Fig. 13. SEM images of the metakaolin mortar mixtures (E: Ettringite).
Fig. 14. SEM images of the silica fume mortar mixtures (E: Ettringite).
estimated by using the proposed equation. However, for the mixtures exposed to the magnesium sulfate solution, there was not a
strong relationship between expansion and the other parameters.
The coefcient of correlation in the case of MgSO4 exposure was
found to be 0.43. This may be due to the fact that magnesium sulfate attack in addition to ettringite and gypsum formation expansion causes a loss of mass due to CSH destruction. It should be
emphasized that the equation is valid for the materials and the
mixtures used as well as the test conditions applied in this study.
3.6. Freezingthaw resistance
The weight change (at every 30 freezethaw cycles), the compressive strength reduction and relationship between weight loss
and water absorption of the mortar mixtures after 300 cycles of
freezingthawing are shown in Figs. 1618, respectively. At the
end of 300 cycles, the reduction in compressive strength of the
control, y ash, metakaolin and silica fume mixtures were 26%,
18%, 11% and 7%, respectively. The weight loss for these mixtures
was 1.36%, 1.05%, 0.7% and 0.48%, respectively. The weight loss of
the specimen increased with increasing of the microcracks and
scaling due to freezethaw cycles. Test results demonstrated that
the mixture containing silica fume had the best performance
against frost action. It should be mentioned that no air entraining
agent was used in the mixtures.
It is known that the degree of saturation of the material plays an
important role in the freezingthawing behavior. Thus, the transport properties can be a good measure of the freezingthawing
resistance of the material [40]. Transport properties test results
indicated that the permeability of the mortar mixtures decreased
by using of the mineral admixtures. Moreover, the mixture containing silica fume had the best transport properties compared to
the other pozzolanic mortars. As it was mentioned earlier, cement
replacement by silica fume resulted in a 75% reduction in the chloride ion penetration of the mortar. As it can be seen from Fig. 18,
the weight loss of the mortar mixtures exposed to 300 freezethaw
24
Gypsum (X)
Ettringite (XX)
1.4
Control
1.2
50
100
150
200
250
300
Fig. 16. Weight loss percentage of all mixtures during freezingthawing cycles.
26
18
11
7
10% FA
10% MK
y = 2.4657x + 0.762
r = 0.9672
1
0.3
0.5
0.7
0.9
1.1
1.3
1.5
Control
10% SF
Fig. 17. Compressive strength reduction percentage of mortar mixtures after 300
freezethaw cycles.
Fig. 18. Relationship between weight change after 300 cycles of freezing and
thawing and water absorption of mortar mixtures.
Acknowledgement
The authors would like to thank Izmir Baticim cement plant
authorities for their kind assistance in providing the cement as
well as determining the chemical composition of the cement.
References
[1] Mehta PK, Monteiro PJM. Concrete; microstructure, properties, and material.
3r ed. New York, USA: McGraw-Hill; 2006.
[2] Neville AM, Brooks JJ. Concrete technology. 2nd ed. UK: Longman; 2010.
[3] Malhotra VM, Ramachandran VS, Feldman RF, Aitcin PC. Condensed silica fume
in concrete. Boca Raton, FL: CRC Press; 1987.
[4] Swamy RN. Cement replacement materials. Blackir and Son, London: Surrey
University Press; 1986.
[5] Inan Sezer G. Compressive strength and sulfate resistance of limestone and/or
silica fume mortars. Const Build Mater 2012;26(1):6138.
[6] Giner VT, Ivorra S, Baeza FJ, Zornoza E, Ferrer B. Silica fume admixture effect on
the dynamic properties of concrete. Const Build Mater 2011;25(8):32727.
[7] Siddique R, Klaus J. Inuence of metakaolin on the properties of mortar and
concrete: a review. Appl Clay Sci 2009;43:392400.
[8] Neville AM. Properties of concrete. 4th ed. UK: Longman; 1995.
[9] Felekoglu B, Trkel S, Kalyoncu H. Optimization of neness to maximize the
strength activity of high-calcium ground y ash Portland cement composites.
Const Build Mater 2009;23(5):205361.
[10] Mardani-Aghabaglou A, Ramyar K. Mechanical properties of high-volume y
ash roller compacted concrete designed by maximum density method. Const
Build Mater 2013;38:35664.
[11] Mardani-Aghabaglou A, Andi-akir , Ramyar K. Freezethaw resistance and
transport properties of high-volume y ash roller compacted concrete
designed by maximum density method. Cem Concr Compos 2013;37:25966.
[12] Vuk T, Gabrovek R, Kaucic V. The inuence of mineral admixtures on sulfate
resistance of limestone cement pastes aged in cold MgSO4 solution. Cem Concr
Res 2002;32(6):9438.
[13] Atahan HN, Dikme D. Use of mineral admixtures for enhanced resistance
against sulfate attack. Const Build Mater 2011;25(8):34507.
[14] Aydn S, Yazc H, Yigiter H, Baradan B. Sulfuric acid resistance of high-volume
y ash concrete. Build Environ 2007;42(2):71721.
[15] Shafaatiana SMH, Akhavanb A, Maraghechib H, Rajabipourc F. How does y
ash mitigate alkalisilica reaction (ASR) in accelerated mortar bar test (ASTM
C1567)? Cem Concr Compos 2013;37:14353.
[16] Shia X, Yanga Z, Liua Y, Doug Cross D. Strength and corrosion properties of
Portland cement mortar and concrete with mineral admixtures. Const Build
Mater 2011;25(8):324556.
[17] Yang CC, Wang LC. The diffusion characteristic of concrete with mineral
admixtures between salt ponding test and accelerated chloride migration test.
Mater Chem Phys 2004;85(23):26672.
25