Introduction
In the cement manufacturing process, carbon dioxide is released, and the wastes and by-products produced in other industries are used as raw materials and heat energy. The “Long-term Vision of the Cement Industry Aiming for Carbon Neutrality” announced by the Japan Cement Association reported that the cement industry used approximately 27 million metric ton of waste in FY 2018, which comprised approximately 11% of the recycled resources of Japan, and this effort has contributed to the construction of a sound material cycle society [
1]. In addition, it has been reported that waste plastics, which will be difficult to dispose of overseas in the future, can be used as a substitute for thermal energy, further contributing to the sound material cycle society. Moreover, according to the estimates by the Japan Cement Association, acceptance of waste and by-products in the cement industry is expected to extend the life of final industrial waste disposal sites by approximately 11 years [
1].
According to the carbon neutral strategy developed by Global Cement and Concrete Association (GCCA), it is important to reduce the amount of cement clinker production to reduce CO
2 emissions [
2]. On the other hand, the establishment of Carbon dioxide Capture, Utilization and Storage (CCUS) has the potential to greatly contribute to the reduction in CO
2 emission, and this technology is being developed as an essential technology for achieving carbon neutral in the cement and concrete fields. In addition, in Japan, on the website of the Agency for Natural Resources and Energy, it has been recommended that the CCUS in the clinker manufacturing process develop to achieve both reduction of CO
2 emissions and resource recycling in the cement industry [
3]. If this technology is established, CO
2 emissions in the clinker manufacturing process will be reduced to almost zero. Therefore, it can be considered that clinker purely contributes to resource recycling if this technology is established in the future.
However, it is a fact that the domestic demand for cement is on the decline due to the maturation of social-infrastructure development. Therefore, if the clinker production were to shrink before CCUS was developed in the cement industry, more industrial waste would end up in landfills. To solve this problem, it is necessary to take new measures other than using cement as a binder to secure a certain amount of cement clinker production from the present.
Some research teams have focused on cement clinker, which is an intermediate product of cement, and investigated various basic physical properties of concrete and mortar that used cement clinker as a fine aggregate [
3‐
5,
5]. These studies have clarified that mortar with cement clinker fine aggregate (CL) has excellent strength development and chloride ion transfer resistance [
3]. Even when using fly ash (FA) as a binder, it could ensure the strength development of mortar using CL [
5]. In addition, from the point of view of reducing the heat produced during the hydration reaction, the combination of FA and CL was valid [
5].
However, alkali–silica reaction (ASR) mortar bar tests have shown that, when a part of cement was replaced by FA, mortars that used CL and andesite (An) as fine aggregate have a lower ASR-suppressing effect of FA than mortars that used limestone fine aggregate (LS) and An [
5]. As per Miyamoto et al., it was considered that pH in a mortar increased due to the leaching of alkali from CL. Therefore, it was hypothesized that replacing cement with higher quantities of FA will lower the pH in mortar and improve an ASR-suppressing effect of FA. However, increasing the replacement ratio of FA may decrease the early age strength development of mortar.
Meanwhile, using CL increases the heat quantity associated with hydration [
5]; therefore, it was considered that using CL can reduce the energy required for high-temperature steam curing for precast concrete (henceforth referred to as PCa). Furthermore, CL improves initial strength, which may enable early mould removal of PCa products. These advantages allow CL to support the dissemination of PCa products. Furthermore, the Ministry of Land, Infrastructure, Transport and Tourism has recommended the commercialization of PCa in concrete structures to improve productivity in the construction industry. In this regard, using CL is expected to contribute to resolving the labor shortage in the construction industry caused by the impending declining birth rate and aging population of Japan.
However, PCa products are a possibility that undergoes expansion and cracking due to DEF (Delayed Ettringite Formation.) DEF-induced expansion cracks can be occasionally seen on the hardened concrete which has a history of being subjected to high temperature during its hardening, such as high-temperature steam curing [
6‐
9]. Expansion due to DEF is strongly related to the formation of ettringite as a secondary mineral. In addition to the high-temperature history of concrete, another factor that causes DEF is a decrease in pH of the pore solution. A pore solution of concrete has high pH at the time of manufacturing; however, pH of pore solution decreases over time in an environment where exposed by water. Ettringite tends to be produced at a pH of approximately 12, which is lower than the pH inside normal concrete [
10‐
12], and decreased pore solution pH may promote the secondary formation of ettringite. Previous studies have shown that CL supplies alkali to pore solution [
5]. Therefore, it was considered that pH of pore solution is possibility supress the decrease with this effect, thereby suppressing DEF.
Based on the above background, in this study, it was investigated that the strength development and ASR-induced expansion suppression effect of mortar that substituting cement by FA up to 80% and used CL. In addition, the DEF-induced expansion suppression effect of the mortar that used CL was verified in this study.
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