Effect of accelerated carbonation on the microstructure and physical properties of hybrid fiber-cement composites
Introduction
Fiber-cement products have been widely used in the world due to their versatility for manufacturing construction materials, such as flat boards for walls, corrugated sheets and water tanks, present in most of houses in developing regions as well as in agricultural and industrial buildings (Ikai et al., 2010).
The restrictions in the use of asbestos led to the investigation of alternative reinforcing and processing fibers, such as vegetable and synthetic fibers. Vegetable fibers are widely available in most developing countries and present several interesting characteristics such as low density, renewable character, biodegradability and availability at low cost and in a wide variety of morphologies and aspect ratios. On the other hand, synthetic fibers are developed from fossil fuels and there is a concern by the fiber-cement industries about the availability of these fibers to the current market demand and about the high costs (as high as approximately 40% of the total cost of raw materials), which can make it impracticable for fiber-cement production at affordable costs. Reducing the content of synthetic fibers is an effective way to reduce production costs in air-cured fiber-cement products (Dias et al., 2010).
One of the drawbacks in the use of vegetable/cellulose fibers is their mineralization in the high alkali Portland cement matrix, with the pH around 13. Mineralization of the cellulose fibers is caused by the free ions from the dissolution of Portland cement phases that penetrated into the fiber cavity (lumen), leading to the re-precipitation of ettringite/monosulphate and calcium hydroxide into the fiber and inducing the stiffening of the cellulose fibers. Secondary (re-precipitated) ettringite formation has been previously suggested as one of the degradation mechanisms of pulp fiber into cement matrix (Mohr et al., 2005, Mohr et al., 2006). This low durability of the vegetable fibers in the cementitious matrix causes reduction of the mechanical performance of the fiber-cement composites due to the fiber mineralization and loss of adhesion between fiber and matrix (Mohr et al., 2005, Tonoli et al., 2010). Hence, the optimal situation would be to protect the cellulose fibers from mineralization with a less aggressive matrix, maintaining the fiber strength and the quality of the fiber bridging that guarantee composite ductility.
Accelerated carbonation of the cement matrix can be employed to improve the durability of the cellulose fiber-cement composites, because it reduces the alkalinity of the cement matrix, lowering the pH, and making it less aggressive to the cellulose fibers (Toledo Filho et al., 2003). Also, the consequences of carbonation on cement are the stability of the chemical hydration products and mechanical properties (Soroushian et al., 2012); densification of the cementitious matrix and reduction of its permeability (capillary) and porosity, which constitutes a positive process with respect to the sealing quality of the cement (Lesti et al., 2013). The carbonation is the reaction of cement hydration products with carbon dioxide (CO2), which could represent great impact on the sustainable growth of the construction industry in the future (Silva et al., 2009).
In fiber-cement composites, the carbonation of the matrix is enhanced due to its high porosity in consequence of the fibers effect, which facilitates the penetration of CO2 within the composite. In a previous study, Tonoli et al. (2010) evaluated the effect of accelerated carbonation, applied after 28 days of cure, on the durability of cellulose fiber-cement composites. They concluded that this procedure improved the initial mechanical strength, decreased the calcium hydroxide content and led to a denser matrix, but the embrittlement of the composites after severe aging was not avoided. That study showed the necessity to anticipate the fast carbonation for initial periods of cure, which would not allow time for the alkali to attack the cellulose fibers during the cement hydration. Therefore, the present work contributes to the widespread use of accelerated carbonation as a way to mitigate cellulose degradation into the fiber-cement composites. However, there is still a lack of information about the changes promoted by the accelerated carbonation on the performance and microstructure of hybrid (reinforced with cellulose and synthetic fibers) fiber-cement composites.
The dissemination of the use of accelerated carbonation during the initial cure fits well with the growing necessity of more sustainable technologies and raw-materials, which is associated to the consume of the CO2 emissions eventually generated by the industrial processes, and allows partial substitution of the more expensive petroleum derivative polymer fibers used to retain the durability of the composites under aggressive climatic conditions. According to Soroushian et al. (2012), CO2 curing of cellulose fiber-cement has also shown to enhance productivity and engineering properties (including dimensional stability) of the end product.
Carbonation can occur in use naturally by the reaction between alkaline matrix of the fiber-cement and atmospheric CO2, but the natural reaction is very slow. Then, accelerated carbonation can complete its reaction within hours and has been proposed as an alternative technology to the natural carbonation (Lim et al., 2010). In this context, the aim of this work was to evaluate the effect of accelerated carbonation on the microstructure and physical properties of fiber-cement composites with hybrid reinforcement.
Section snippets
Sampling and accelerated carbonation
The fiber-cement samples with nominal thickness of 4 mm were obtained from the Hatschek process. The Hatschek process is the most employed one in producing fiber cement components, and consists of producing fiber-cement boards by assembling thin layers (up to 1 mm) made from a suspension of Portland cement, mineral admixtures (limestone filler for example), fibers (cellulose and synthetic fibers) and water. Vacuum is applied to remove water from the layer before it is transferred to the formation
Evaluation of the accelerated carbonation
Fig. 1 depicts the mass loss (TG) and differential weight loss (DTG) of the composites at the different carbonation conditions. During the sample preparation (milling) for TG analysis, the PVA fibers were removed from the powder sample by screening. This is the explanation for no observation of the decomposition peak between 225 and 295 °C related to PVA fibers.
The temperature range between 295 and 370 °C corresponds to the degradation of the cellulose fibers, and no changes were observed between
Conclusion
Accelerated carbonation is presented here as a good initiative to CO2 sequestration and an interesting way to prematurely decrease the alkalinity of the cement matrix by consumption of the Ca(OH)2 ions in the cement paste, resulting in the densification of the matrix and in lower porosity. The consumption of C–S–H and calcium sulfoaluminates (e.g. ettringite) was also observed during the accelerated carbonation. The SEM micrographs show that the CaCO3 formed from the carbonation reaction is
Acknowledgments
Thanks to Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq), Fundação de Amparo à Pesquisa do Estado de São Paulo (Fapesp), Fundação de Amparo à Pesquisa do Estado de Minas Gerais (FAPEMIG), Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (Capes), Infibra Ltda., Imbralit Ltda., and Rede Brasileira de Compósitos e Nanocompósitos Lignocelulósicos (RELIGAR), in Brazil.
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