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The thaumasite form of sulfate attack (TSA) is a unique distress mechanism in portland cement concrete in which thaumasite formation (TF) alters the primary binder, calcium silicate hydrate (CSH), in addition to calcium hydroxide and calcium aluminate hydrates. TSA in concrete may cause loss of paste-aggregate bond, strength, coherence, and eventually serviceability. The time frame of TSA can be as short as a couple of years. Reported TSA cases have mostly involved sulfate from external sources. This paper presents two less common TSA cases, in which sulfate was determined to be from an internal source: in one case, from dolostone coarse aggregate and in the second case from the cementing material. Characteristics of TSA distress and the composition and texture of the concrete are discussed, and these cases are compared with other reported internal and external TSA cases. It is concluded that petrographic examination of the concrete, particularly using thin-sections, provides the most definitive diagnosis of TSA. Significant implications of findings from the two case studies regarding mechanisms of thaumasite formation and potential propensity of portland-limestone cement for TSA are also discussed.
Construction and Building Materials, 2013
h i g h l i g h t s " The resistance of a plain Portland cement and a Portland-limestone cement to sulfate attack at 5°C was evaluated. " The mortar bars showed deterioration in the form of cracking and spalling, and expansion first. " Eventually, the samples lost cohesiveness and turned into a white, pulpy mush called thaumasite. " The expansion due to the formation of ettringite and gypsum preceded the formation of thaumasite. " Portland-limestone cements are susceptible to the thaumasite form of sulfate attack at 5°C.
Synopsis: Paste and mortar specimens were manufactured by using ordinary portland cement (OPC), C 3 A-free portland cement, slag cement and pozzolan cement. A carbonaceous or siliceous filler (10% by cement weight) was blended with each of the above portland cements. Limestone or quartz sands were used for mortar mixtures. Four different water-cement ratios (w/c) were adopted: 0.55, 0.50, 0.45, and 0.40. After a 28-day wet curing, paste and mortar specimens were immersed in MgSO 4 aqueous solutions with a SO = 4 concentration of 350, 750, and 3000 mg/l, corresponding to chemically aggressive exposures 5a, 5b, and 5c respectively, according to the European Norms (ENV 206). The deterioration of cement paste specimens was studied by X-ray diffraction analysis to detect ettringite and/or thaumasite formation in relationship with the visual observation of sulfate attack. The deterioration of mortar specimens was studied by measuring elastic modulus and compressive strength at different periods of aggressive exposure (from 1 month to 5 years). After 5 years of exposure to the sulfate attack, paste and mortar specimens with slag and pozzolan cements were undamaged independent of the sulfate concentration, sand type, and w/c. On the other hand, paste and mortar specimens with blended limestone-portland cements showed surface damage when exposed to the 3000 mg/l of SO = 4 aqueous solution. However, they did not show loss of either compressive strength or elastic modulus in the 5 years of sulfate exposure. The surface damage was mitigated when OPC was replaced by the C 3 A-free portland cement and completely eliminated when this cement was blended with a siliceous filler rather than with a limestone case. Thaumasite and ettringite are responsible for the surface attack. The amount of thaumasite was a little higher in the presence of blended limestone portland cement.
Cement and Concrete Composites, 2002
Four series of micrographs are presented illustrating the microstructures resulting from the long-term immersion (21 years) in sulfate solutions of concretes prepared using either a Type II or a Type V Portland cement. The effects of cement type (II or V), water-to-cement ratio (0.45 or 0.50) and the sulfate solution (Na 2 SO 4 or MgSO 4) on microstructural evolution were analyzed. Gradients were observed in sulfate-containing solids from the concrete surfaces inward. Such gradients are consistent with immersion in sulfate solutions in that the extent of sulfate attack was progressively diminished at locations increasingly remote from the surfaces. Although the samples were stored at ambient temperatures, extensive thaumasite formation was observed.
This paper presents an investigation on the mechanism of sulfate attack on Portland cements (PCs) containing limestone filler. It is based on the analysis of microstructure and composition of mortar specimens (ASTM C 1012) stored for 2 years in sodium sulfate solution (0.352 M). Microstructure was studied using quantitative X-ray diffraction (XRD) on samples taken from the surface to the core of the specimens. The profile of compounds formed by sulfate attack was determined millimeter by millimeter at 1 and 2 years. Results show that sulfate attack in mortars containing limestone filler is characterized by an inward movement of the reaction front leading first to the formation of ettringite, later to gypsum deposition, and finally to thaumasite formation when the decalcification of mortar leads to the breakdown of C-S-H. D
Cement and Concrete Composites, 2003
The thaumasite form of sulfate attack (TSA), is a deleterious physico-chemical attack of the calcium silicate hydrate (C-S-H), binding phase of concrete. Water:binder ratios (w:b), are known to control ingress of potentially deleterious ions by pore structure refinement at low (0.40) values. Equally, a physical-chemical barrier exists at about w:b ratio of 0.45 regardless of the binder type. The inclusion of ultra-fine pozzalans (e.g. metakaolin) in the binder has been shown to impart such properties through densification of the matrix and removal of calcium hydroxide.
2004
Chlorides have been reported to be present in several field cases where thaumasite attack has occurred. However, no published systematic research dealing with the role of chloride in the thaumasite form of sulfate attack could be found in the literature. This research project has been designed through a comprehensive experimental programme to address this issue. This investigation studies the following: the formation of thaumasite in long-term exposure of carbonated systems to sulfate environment; whether or not the presence of chloride affects the thaumasite form of sulfate attack (TSA); the effect of long-term and short-term carbonation on the precipitation of thaumasite; the composition of thaumasite formed in chloride containing solutions; the chloride binding capacity of thaumasite-affected cement matrix; and the use of metakaolin to prevent TSA in carbonated mortar. Mortar samples were cast using siliceous sand and Portland cement replaced by different amounts (0,5 and 15%) of limestone filler, and by 10% metakaolin. Mortar cubes were subsequently stored in deionised water, magnesium sulfate solution, combined sulfate and sodium chloride solution and simulated seawater at 5°C and 20°C. Long-term specimens consisted of Portland cement mortars containing 15% limestone filler, which were exposed to atmospheric carbonation at 5 and 20°C for 5 years, were also immersed in these salt solutions at both temperatures. The mortar cubes were examined regularly every month, and the results of visual assessment recorded. The mineralogy of the deteriorated products was determined by x-ray diffraction (XRD), infrared spectroscopy (IRS). The pH of the solutions was also measured periodically. The composition of the thaumasite and the deteriorated cement matrix was assessed by means of the determination of the unit cell parameters of the crystal, by quantitative infrared spectroscopy (IRS); scanning electron microscopy (SEM); backscattered 1.2. Structure of the thesis 3 2. Chapter Two 5-2.4.4 The use of metakaolin replacing cement to prevent TSA 30 2.5 Concluding remarks iii 3 Chapter Three 34 Experimental Programme 3.1 Introduction 34 3.2 Experimental design 34 3.3 Materials 3.1.2 Characterisation 3.4 Mortar mixes and casting 3.5 Long term samples 38 3.6 Test Solutions 3.7 Visual inspection 3.8 Mass change 3.9 X-ray diffraction and Infrared spectroscopy sample preparation 3.9.1 XRD 3.9.2 Infrared Spectroscopy (IRS) 3.10 Scanning Electron Microscopy and X-Ray Microanalysis 3.11 pH changes 46 3.12 Statistical analysis 46 4. Chapter Four 48 Microstructure of 5-Year Old Mortars Containing Limestone Filler Damaged by Thaumasite 4.1 Abstract 48 4.2 Introduction 49 4.3 Experimental Work 50 4.4 Results and Discussion 51 4.2.1 Control OPC Mortar 51 4.2.2 Mortar with 5% limestone filler 55 4.2.3 Mortar with 15% limestone filler 57 4.2.4 Mortar with 35% limestone filler 61 4.2.5 Progress of TSA as a function of limestone content and period of exposure 64 4.5 Conclusions 65 iv 5 Chapter Five 66 Performance of Limestone Filler and Metakaolin Containing Portland Cement Mortars under Combined Chloride and Sulfate Exposure 5.1 Abstract 5.2 Introduction 5.2.1 Evidence to suggest that chloride plays a role in TSA A. Field cases B. Laboratory studies 5.2.2 Summary 5.3 Res ults 71 5.3.1 Visual Assessment 72 A. Up to 12 weeks 72 B. After 24 weeks C. After 44 weeks D. After 53 weeks E Seawater 81 F. Long term specimens 82 5.3.2 Mass loss in salt solutions 85 5.3.3 Mineralogy of deteriorated products 88 A. X Ray Diffraction (XRD) 89 B. IR Spectra 102 5.3.4 Effect of combined chloride and sulfate on the pH 111 A. 15% Limestone Filler 113 5.4 Discussion 122 5.4.1 Evidence suggesting a detrimental role for chloride in thaumasite formation 122 5.4.2 The effect of carbonation on TSA 125 5.4.3 The effect of chloride in the thaumasite form of sulfate attack in seawater 125 5.4.4 The use of metakaolin to prevent TSA 126 5.4.5 Effect of chloride on the pH profile in the presence of carbonates and sulfates 127 5.4.6 Mechanism by which chlorides affect TSA 129 5.5 Conclusions 134 V 6. Chapter Six 137 Effect of Combined Chloride and Sulfate on TSA: Microstructure and Micro-Analytical Results 6.1 Abstract 6.2 Introduction 138 6.3 Results 6.3.1 Microstructure of TSA in 15%LF samples in salt solutions at 5°C 142 A. 15% limestone filler in 0.60% S04 at 5°C 142 B. 15% limestone filler in 0.60% SO4 and 0.50 %Cl' at 5°C 145 C. 15% limestone filler in 0.60% SO'and 1.0% C1 at 5°C 148 D. 15% limestone filler in 0.60% SO 4-and 2.0% Cl' at 5°C 150 6.3.2 Characteristics of thaumasite in salt solutions A. Energy Dispersive X-ray 152 B. Quantitative X-ray microanalysis 156 C. Unit cell parameters 159 D. Infrared Spectroscopy (IRS) E. Sumary 177 6.3.3 Chloride binding capacity of Portland cement mortar containing limestone filler in salt solutions A. 15% limestone filler in 0.60% SO42' at 5°C B. 15% limestone filler in 0.6% SO4 and 0.5 %Cl' at 5°C 180 C. 15% limestone filler in 0.60% SO4 and 1.0% Cl' at 5°C D. 15% limestone filler in 0.60% SO4 and 2.0% Cl at 5°C 184 6.3.4 Chloride and magnesium profiles in 15%LF samples in salt solution at 5°C 187 A. 15% limestone filler in 0.60% S04at 5°C 187 B. 15% limestone filler in 0.60% SOäand 0.5 %Cl' at 5°C 189 C. 15% limestone filler in 0.60% SOäand 1.0% Cl' at 5°C 192 D. 15% limestone filler in 0.60% SO4and 2.0% Cl at 5°C 193 6.4 Discussion 196 6.4.1. Microstructural features of TSA in mortars containing limestone filler immersed in combined sulfate chloride solutions at 5°C 196 6.4.2 Effect of chloride on the composition of thaumasite 197 A. EDX/ X-ray microanalysis 197 B. Unit cell parameters 198 C. IRS 201 6.4.3. Effect of chloride on the chemical alterations of cement matrix due to TSA 202 A. Silicon profile 203 B. Aluminium profile 206 C. Sulfate profile 207 D. Chloride and magnesium profiles in mortar containing limestone filler immersed in combined sulfate and chloride solutions at 5°C. 210 6.5. Conclusions 213 V1 7. Chapter Seven Effect of Combined Chloride and Sulfate on TSA: Overall Discussion 7.1 Discussion 216 7.1.1 The effect of carbonate content on the microstructure changes in Portland cement mortars to TSA 7.1.2 The effect of atmospheric carbonation on the formation of thaumasite 7.1.3 The role of chloride in TSA: Damage assessment, characterization of deterioration products and main factors 220 7.1.4 The use of metakaolin in mortar containing limestone filler to prevent TSA221 7.1.5 Composition of thaumasite in the presence of chlorides 7.1.6 Chloride binding capacity and interaction in thaumasite attacked Portland cement matrix 7.1.7 Effect of pH on TSA 7.1.8 Mechanisms by which chloride affect thaumasite precipitation in Portland cement A. Carbonate system 226 B. Silicate system C Catalytic role of chloride in thaumasite formation 230 D. Summary 232 E. Damage assessment 235 8. Chapter Eight 237 Overall Conclusions 8.1 Overall Conclusions 237 8.2 Recommendations for future research References
2017
The present work reports the results of an experim ental campaign started two years ago and still ongoing, aimed to assess the behavior of different cementitious materials subject to external sulfate attack. To this purpose prismatic specimens of cement paste and specimens of mortar and concrete produced with the same Portland cement, were immersed in demineralized water and in different solutions containing 5% and 10% sodium sulfates. The expansion was monitored in time by direct length measurements and the degradation of the stiffness was indirectly obtained through non-destructive ultrasound wave pr opagation tests. XRD tests and SEM observations evidenced the presence of secondary gy psum in the outer part of the specimens were sulfates penetrated. An increase of the material po rosity was also measured in this region.
This paper will illustrate the value of concrete petrography through two case studies. The first case involves a municipal concrete building in Michigan that exhibits substantial foundation expansion and cracking. Petrographic examination indicates that the distress is attributed to thaumasite sulfate attack (TSA), based on the presence of cracks, microcracks and ring gaps around aggregates filled with abundant thaumasite secondary deposits, and observed paste alteration to thaumasite. Petrographic examination also reveals the sulfate is internally sourced, from the dolomite coarse aggregate in the concrete. To the best of our knowledge, TSA due to an internal sulfate source from aggregate has not been reported so far. The second case involves concrete walls of a sewer tunnel about 100 years old. The exposed sides of the inner walls have experienced significant deterioration and spalls. Petrographic examination revealed that concrete deterioration is due to sulfate attack associated with accumulation of hydrogen sulfide (H2S) gas within the structure. Distinct physical, compositional, and textural variations in paste along the exposed surface are observed. Depth of deterioration has been determined to be shallow from the existing surface, although the nearsurface damage is severe.
Cement and Concrete Composites, 2003
Thaumasite formation and limited thaumasite sulfate attack has recently been discovered in sprayed concretes in contact with pyrrhotite-, pyrite-and calcite bearing Alum Shale in Oslo. In concretes, several types of calcite occur, including internal Popcorn calcite formed by replacement of both thaumasite and calcium silicate hydrate. In an attempt to throw further light on the origin of carbonates and sulfates involved, we have used the laser ablation probe to characterise these secondary minerals with respect to stable isotopes (C, O and S). Mitigation as well as repair may in several cases depend much on correct characterisation and location of the fluids provenance, and stable isotopic characterisation may be an appropriate tool to do so.
Cement and Concrete Composites, 2003
There is disagreement about the role of sulfuric acid in the thaumasite form of sulfate attack (TSA) of concrete. Some researchers suggest that thaumasite is formed only at pH above 10.5, whereas others report that the primary cause of deterioration in the affected M5 bridge foundations was sulfuric acid attack followed by neutral TSA. The aim of this work is to reconcile these conflicting views by undertaking parallel studies of concrete exposed to aggressive acid and sulfate solutions and concrete/clay interface work using weathered Lower Lias clay. Concrete specimens have been exposed to BRE Digest 363 sulfate class solutions and acidic and acidic-sulfate solutions at 4.5 ± 0.5°C. Selected samples are being characterised at intervals up to 5 years. At this stage, results are reported for 5-month samples. Various binders including Portland cement, Portland-limestone cement, blastfurnace slag cement, pulverized-fuel ash cement and sulfate-resisting Portland cement at water/binder ratios (w/b) from 0.35 to 0.5 have been studied. Initial visual observations and X-ray diffraction analyses have identified thaumasite in some of the systems after 5 months immersion in solution. An overview of the ongoing parallel concrete/clay interaction work is also presented to contextualise the concrete work.
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