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Research Article
2025
:37;
10282025
doi:
10.25259/JKSUS_1028_2025

Environmental-friendly high-strength concrete using hydraulic cement and river gravel residue

Faculty of Industrial Technology, Uttaradit Rajabhat University, Uttaradit 53000, Thailand
School of Civil Engineering, and Center of Excellence in Innovation for Sustainable Infrastructure Development, Suranaree University of Technology, Nakhon Ratchasima 30000, Thailand
Academy of Science, The Royal Society of Thailand, Bangkok, 10210, Thailand
School of Internal Medicine, Suranaree University of Technology, Nakhon Ratchasima 30000, Thailand
Department of Civil and Construction Engineering, Swinburne University of Technology, Hawthorn, Victoria 3122, Australia

* Corresponding author: E-mail address: suksun@g.sut.ac.th (S Horpibulsuk)

Licence
This is an open-access article distributed under the terms of the Creative Commons Attribution-Non Commercial-Share Alike 4.0 License, which allows others to remix, transform, and build upon the work non-commercially, as long as the author is credited and the new creations are licensed under the identical terms.

Abstract

This research investigated the use of hydraulic cement (HC) and river gravel residue for the manufacture of high-strength concrete. HC with fly ash (FA) replacement at levels of 0%, 10%, 20%, and 30% was used as a binder, whilst a cost-effective mid-range water-reducing admixture (MRWR) was used to improve workability and enhance compressive strength of the mix. The river gravel residue from the construction sand production process was used as coarse aggregate. The concrete mix design followed ACI 211.4R-93, targeting a compressive strength of 60 MPa at 28 days. Effects of FA content and MRWR content on workability, compressive strength, and temperature variations during hydration were investigated in this research. The optimum FA replacement for the highest compressive strength was achieved at 20% and the MRWR was at 1.5%. The river gravel residue was proven to be an effective aggregate, improving workability and contributing to steady strength development. The novelty of this study lies in the use of river gravel, a locally available aggregate, in combination with HC containing pozzolanic constituents. With the addition of an appropriate level of FA and a cost-effective MRWR, high-strength concrete can be produced without relying on expensive high-range water-reducing admixture, providing a sustainable and practical solution for engineering applications.

Keywords

Fly ash
High-strength concrete
Hydraulic cement
River gravel residue
Sustainable material

1. Introduction

The growth of society has led to an increasing demand for housing and infrastructure. In large cities, optimizing land use has become crucial, resulting in the expansion of high-rise residential buildings, especially in economic zones. High-strength concrete (HSC), which offers greater strength compared to conventional concrete (ACI 363R-92, 2000), is widely used in the construction of high-rise buildings and large-scale infrastructure. HSC relies heavily on cement as a critical component, requiring significantly higher cement content than conventional concrete. However, the traditional production process of Portland cement significantly contributes to carbon dioxide (CO2) emissions, accounting for approximately 8% of global CO2 emissions (Fernandez-Jimenez et al., 2006; Brandão Ferreira, 2014). This increased cement demand results in substantially higher carbon dioxide (CO₂) emissions during the manufacturing process (Alsalman et al., 2021).

In addition to cement, the use of natural aggregates (sand and gravel) in HSC production accelerates environmental degradation and depletes natural resources at an alarming rate (Mehta & Monteiro, 2014; Celik et al., 2014; Habert et al., 2011). The production of aggregates involves more complex processes, such as repeated crushing, screening, and quality enhancement, to meet the required properties. These processes are highly energy-intensive, leading to significantly greater CO₂ emissions. Furthermore, the transportation of aggregates, often sourced from distant quarries, adds another significant layer of CO₂ emissions attributable to logistics (Sabău et al., 2021; Chindasiriphan et al., 2023).

With growing concerns over sustainability and climate change, research into environmentally friendly concrete technologies has gained increasing attention. In response to these challenges, alternative materials such as hydraulic cement (HC), which offers greater energy efficiency compared to ordinary Portland cement, have emerged as viable solutions (Scrivener et al., 2018; Gartner & Sui, 2018; Pheeraphan, 2021). Studies showed that concrete produced with HC exhibited high durability in various environmental conditions, reducing maintenance requirements and extending the lifespan of concrete structures (Ranjitham et al., 2019; Juenger et al., 2011).

Recent studies have increasingly demonstrated the potential of industrial by-products as supplementary cementitious materials (SCMs) in sustainable concrete production. For instance, rice husk ash (RHA) has been incorporated into lightweight flowable self-compacting concrete (LF-SCC), enhancing durability and reducing chloride penetration (El-Mir et al., 2022). Similarly, sugarcane bagasse ash (SCBA) and fly ash (FA) have been reported to improve compressive strength and refine the microstructural characteristics of concrete (Kannur & Chore, 2021; 2023a; 2023b). More recent investigations on semi-flowable self-compacting concrete incorporating diverse industrial by-products have also demonstrated significant improvements in strength, durability, and microstructural performance, particularly for pavement and highway applications (Kannur & Chore, 2023c; 2024; 2025a; 2025b). Among these materials, FA was selected in the present study because of its high availability, consistent quality, cost-effectiveness, and extensively documented pozzolanic activity. Numerous studies have confirmed that FA reduces calcium hydroxide formation while promoting the development of calcium silicate hydrate (C–S–H) and calcium aluminosilicate hydrate (C–A–S–H) gels, resulting in a denser matrix and enhanced long-term durability. This rationale directly supports the objective of this study, which is to develop sustainable HSC by incorporating FA in combination with HC, river gravel residue, and mid-range water-reducing admixture (MRWR).

River gravel residue, a by-product of sand production in the construction industry, can serve as a sustainable coarse aggregate alternative to mined stone. Previous studies reported that natural river gravel with a round shape enhances concrete workability while minimizing the environmental impact of aggregate extraction (Schneider et al., 2011; Prusty et al., 2016). A study investigated the effects of aggregate types on the compressive strength of concrete, focusing on three coarse aggregate types: quartzite, granite, and natural river gravel. The findings indicated that concrete made with natural river gravel exhibited the highest workability, followed by quartzite and granite. In terms of compressive strength, concrete containing quartzite achieved the highest values across all curing ages, followed by natural river gravel and granite, respectively (Abdullahi, 2012). Further research on river gravel as an alternative to crushed stone in concrete production demonstrated that concrete incorporating river gravel exhibited structural performance comparable to, or slightly inferior to, that of concrete made with crushed stone (TrustGod et al., 2022).

Although natural river gravel significantly improves the workability of concrete, blending it with finely crushed stone can enhance compressive strength by up to 20% compared to using either material alone (Usman et al., 2023). A case study on natural river gravel from the Rapti River in Nepal highlighted its suitability for concrete pavement production, with properties that conform to international quality standards (Maharjan & Tamrakar, 2007). However, a comparative study between natural river gravel from the Brantas River and crushed stone revealed that concrete made with natural river gravel exhibited slightly lower compressive strength than concrete produced with crushed stone (Limantara et al., 2018). These findings suggest that natural river gravel can be a viable alternative for concrete production, particularly for lightweight load-bearing structures and substructures.

Thailand possesses abundant natural resources, leading to the widespread use of crushed stone materials, such as granite and limestone, in the concrete industry. Conversely, river gravel residue, a by-product of sand extraction from rivers, is often overlooked and underutilized. This gravel residue is typically stockpiled in large quantities due to the preference for readily available mountain stone in Thailand’s construction industry, resulting in inefficient resource utilization and increased negative environmental impact.

To address this challenge, this study explores the application of river gravel residue in manufacturing HSC. The approach involves combining river gravel residue with HC, a material that reduces greenhouse gas emissions during production compared to ordinary Portland cement. This combination not only adds value to an otherwise discarded resource but also enhances the technical performance of concrete, making it suitable for high-strength structural applications. Although previous studies have investigated the use of natural river gravel in concrete, most have focused on normal-strength concrete for lightweight or general-purpose structures. This research differentiates itself by emphasizing the utilization of river gravel residue in HSC, a novel application that has not been extensively explored. This innovative approach not only promotes sustainable material usage but also aligns with global efforts to mitigate environmental impacts, supporting the objectives of the Sustainable Development Goals and the Paris Agreement (Van Deventer et al., 2021; Shen et al., 2017).

2. Materials and Methods

2.1 Materials

This study utilized HC as the primary cementing agent, conforming to the Thai Industrial Standard (TIS 2594-2023) to manufacture HSC. A portion of HC was replaced with Class C FA from the Mae Moh power plant at replacement levels of 0%, 10%, 20%, and 30% to improve the chemical reaction of HC. The specific gravities of HC and FA were 3.15 and 2.30, respectively. Additionally, this study employed an MRWR, Types D and G according to ASTM C494, due to its compatibility with FA and its lower cost compared to high-range water reducing admixtures (HRWR). MRWR was found to provide adequate workability and compressive strength development when the mix design was properly optimized. Photos of the raw materials used in this study have been shown in Fig. 1.

Binder mixture.
Fig. 1.
Binder mixture.

Fig. 2 presents scanning electron microscope (SEM) images at 5,000x magnification of HC and FA. The HC particles exhibited irregular shapes with a rough and complex surface texture, while the FA particles were spherical with similarly rough surfaces. The particle size distribution and chemical composition of both materials have been shown in Fig. 1 and Table 1, respectively, with the average equivalent particle sizes (D50) of HC and FA being 15.17 µm and 34.26 µm, respectively. HC primarily contains 12% calcium (Ca) and 6.06% silicon (Si) by weight. FA had a silicon content of 16.68% and an aluminum (Al) content of 9.14%. Both materials included oxygen (O) as a significant component, accounting for 45.38% and 42.03% by weight in HC and FA, respectively. Oxygen plays a crucial role in forming oxide compounds, which enhance the strength of the cement paste.

Particle characteristics of Hydraulic Cement (HC) and Fly Ash (FA).
Fig. 2.
Particle characteristics of Hydraulic Cement (HC) and Fly Ash (FA).
Table 1. Chemical composition of HC and FA from EDS.
Composition HC FA
C 6.07 10.59
O 45.38 42.03
Mg 0.48 1.06
Al 2.06 9.14
Si 6.06 16.86
Ca 39.12 N.D.

The aggregates used in this study consisted of natural river sand and 0.95-mm (3/8-inch) river gravel residue. Both materials were sourced from the Nan River, located in Uttaradit Province, which is a major river in Northern Thailand. The gradation of the river sand complied with ASTM C33 specifications (ASTM, 2002), as illustrated in Fig. 2. The Nan River serves as a significant source of construction materials in the region, highlighting its importance in providing high-quality aggregates for this research.

The particle size distribution analysis revealed that the HC particles had a narrow and consistent distribution, which facilitated hydration and early strength development in concrete. In contrast, FA exhibited a broader, bimodal distribution, efficiently filling voids within the concrete (Fig. 3). The sand had a coarser distribution, enhancing concrete density, reducing voids, and improving overall durability (Assi et al., 2018; Cui et al., 2020; Kim et al., 2022). The aggregate properties used for the mix design have been shown in Table 2.

Particle Distribution of HC, FA, and sand.
Fig. 3.
Particle Distribution of HC, FA, and sand.
Table 2. Aggregate properties test results.
Sand River gravel
GS = 2.64 GS = 2.33
water absorption = 0.36% water absorption = 1.70%
Unit weight (Dense) 1,742 kg/m3 Unit weight (Loose) 1,558 kg/m3
Unit weight (Loose) 1,599 kg/m3 Unit weight (Loose) 1,414 kg/m3
Fineness modulus 2.97 Los angeles abrasion 27.5%

2.2 Preparation of specimens

This study used a concrete mix design based on ACI 211.4R-93 (ASTM, 2000) and targeted a compressive strength of 60 MPa at 28 days. The water-to-binder ratios (w/b) was adjusted to 0.325, 0.320, 0.308, and 0.292, while varying the FA content at 0%, 10%, 20%, and 30% by weight of the binder (HC+FA) to maintain the concrete slump within the range of 75-125 mm (100±25 mm). The mix proportions of the specimens are shown in Table 3. Furthermore, the MRWR content was varied at 1%, 1.5%, 3%, 4.5%, and 6% by total binder weight. These variations were applied using the mix with the optimal FA replacement ratio, which provided the highest compressive strength, to evaluate the effect of MRWR content on compressive strength development and workability.

Table 3. Mix proportions of the specimens (kg/m3).
Mix HC (kg) FA(kg) Sand (kg) Gravel (kg) w/b ratio
HCFA0 551.5 0 1,013 472.7 0.325
HCFA10 496.4 55.1 1,013 472.7 0.320
HCFA20 441.2 110.3 1,013 472.7 0.308
HCFA30 386.1 165.4 1,013 472.7 0.292

2.3 Experimental program

2.3.1 Compression test

Specimen mixing was performed using a rotary drum mixer in accordance with ASTM C192 (ASTM, 2002). After mixing, the fresh concrete was assessed for slump in accordance with ASTM C143 (ASTM, 2002). The preparation of specimens for compressive strength testing involved pouring the fresh concrete into molds with a diameter of 150 mm and a height of 300 mm in three layers, each compacted with 25 blows using a tamping rod. The surface was then leveled, and the specimens were covered with a vinyl sheet and cured at room temperature for 24 h. After demolding, the specimens were submerged in water at 30±2°C for curing. Compressive strength testing was conducted in accordance with ASTM C39 (ASTM, 2002) at curing times of 3, 7, 28, and 56 days.

2.3.2 Temperature measurement

In this test, the cement paste specimens were prepared by mixing and casting into PVC molds with a diameter of 75 mm and a height of 150 mm. A digital thermometer with a probe was positioned at the center of each specimen to monitor temperature variations caused by the chemical reactions of the binder. After placing the specimens in a controlled environment for 24 hours to allow the cement paste to set, the curing process commenced by submerging the specimens in water. Temperature data were recorded daily over a period ranging from 1 to 56 days. The temperature sensors provided an accuracy with a deviation of ±0.383°C. All recorded temperature data were subsequently utilized to compute the standard deviation (SD), where SD/x <10%, with x representing the mean value of the test results

2.3.3 Microstructural analysis

The influence of the w/b ratio, MRWR content and FA replacement ratio on the development of compressive strength of the studied concrete was investigated using SEM in conjunction with energy dispersive X-ray spectroscopy (EDX). Fragments of the 28 days cured samples, obtained from compressive strength tests, were collected for SEM and EDX analyses. These fragments were frozen to prevent moisture loss and then gold-coated prior to analyses (Sukmak et al. 2013). Additionally, the formation of crystals and chemical compounds during the hydration process was further examined using X-ray diffraction (XRD) analysis.

3. Results and Discussion

The following section presents the results and discussion, focusing on three main aspects: compressive strength, temperature variations, and microstructure, which highlight the relationships between mechanical properties, thermal behavior, and the development of the cement paste structure.

3.1 Compressive Strength

Fig. 4 indicates a relationship between compressive strength and curing age for concrete specimens in which HC was partially replaced with various proportions of FA. The compressive strength consistently increases over time for all mixtures. The 28-day compressive strength of HC concretes using limestone and river gravel residue met the strength target (> 60 MPa). However, the 28-day compressive strength of HC-FA concretes remains below the target value of HC concretes. This phenomenon is an expected behavior when incorporating FA. The 56-day results of the 10–20% FA mixes closely approached the target 28-day strength of HC concretes. Nevertheless, optimizing the w/b ratio to achieve appropriate workability has contributed to higher 28-day compressive strength values, reaching 45.9 MPa, 50.8 MPa, and 29.0 MPa for FA replacement levels of 10%, 20%, and 30%, respectively. In contrast, concrete specimens utilizing only HC with limestone (HCFA0) as coarse aggregate achieves 28-day compressive strength exceeding 60 MPa, aligning with the target design strength.

Compressive strength at different curing times and various FA contents.
Fig. 4.
Compressive strength at different curing times and various FA contents.

The use of high volumes of FA results in a reduction of tricalcium silicate (C3S), a key component in the hydration process, thereby limiting the formation of C-S-H, which is responsible for the early development of compressive strength. Consequently, the initial strength development is slower (Chindaprasirt et al., 2007; Rao et al., 2021). FA, as a pozzolanic material, requires calcium hydroxide (Ca(OH)₂) produced from C3S hydration to react and form C-S-H over a longer period. Though, the reduction in C3S content due to FA replacement leads to lower early-age compressive strength, this pozzolanic reaction contributes to improved concrete strength and durability in the long term.

The test results exhibit a consistent trend in compressive strength development across all curing periods. The optimum w/b providing the highest strength is found to be 0.320 for HCFA10 and 0.308 for HCFA20. An increase in FA content from 10% to 20% improves compressive strength. However, replacing more than 20% of cement with FA leads to a decline in compressive strength. This finding corroborates the work of Hemalatha et al. (2017), who identified 20% FA as the optimal replacement level for enhancing concrete strength. The improvement is attributed to the enhanced formation of calcium silicate hydrate (C-S-H), which contributes to the strength and durability of concrete (Sun et al., 2019; Mohsen et al., 2023).

The results of this study indicate that the optimum FA replacement level lies within 10-20%, where compressive strength is maximized. This finding is consistent with previous investigations on self-compacting concrete and semi-flowable self-compacting concrete incorporating FA, SCBA, and RHA, which reported that such pozzolanic materials enhance strength development, particularly at later curing ages, due to their gradual pozzolanic reactivity (El-Mir et al., 2022; Kannur & Chore, 2021; 2023a; 2023b; 2025a). Specifically, studies on pavement concrete and slip-form paving applications have highlighted that an FA content of around 20% represents an optimum range for balancing strength and durability. The present results corroborate these findings, despite the differences in constituent materials; river gravel residue and MRWR were adopted in this study. These factors emphasize the compatibility of FA with alternative aggregates and admixtures for sustainable HSC applications.

While concrete specimens without FA (HCFA0) exhibits stable compressive strength beyond 28 days, specimens incorporating FA (e.g., HCFA20) demonstrate continuous strength development due to the pozzolanic reaction of FA. This reaction, which progresses more slowly than cement hydration, contributes to forming additional calcium silicate hydrate (C-S-H) over time. Consequently, at 56 days, the compressive strength of HCFA20 approaches that of HCFA0, highlighting the long-term benefits of using FA at an optimal replacement level of 20%. These findings align with studies such as Hemalatha et al. (2017), which emphasize the potential of FA in enhancing long-term strength and durability. Replacing more than 20% of the HC with FA significantly reduces the tricalcium silicate (C3S) content in the cement, thus slowing the hydration process and affecting compressive strength development at all curing times.

Fig. 5 illustrates the relationship between compressive strength and curing age for concrete specimens with varying MRWR contents of 1.5%, 3.0%, 4.5%, and 6.0%, designed with an optimum w/b of 0.308 and incorporating a 20% FA replacement ratio. The results demonstrate that MRWR dosages of 1% and 1.5% significantly enhance compressive strength at all curing ages. The specimen with a 1% MRWR content achieves a maximum 7-day compressive strength of 50.8 MPa, demonstrating that this dosage effectively promotes the early hydration process. This behavior can be attributed to the efficient dispersion of cement particles, which enhances the initial formation of C-S-H. However, at curing ages > 7 days, the specimen with a 1.5% MRWR content exhibits the highest compressive strength, reaching 64.6 MPa at 56 days of curing, surpassing the target compressive strength. The superior performance of the 1.5% dosage at later ages can be explained by its ability to retain moisture within the concrete matrix, ensuring prolonged hydration and the continued formation of hydration products over time.

Compressive strength of samples with various MRWR contents at different curing times (w/b = 0.308, FA = 20%).
Fig. 5.
Compressive strength of samples with various MRWR contents at different curing times (w/b = 0.308, FA = 20%).

In contrast, when the MRWR content was increased beyond 1.5%, a noticeable decline in compressive strength was observed across all curing periods. This reduction can be attributed to an imbalance in the w/b ratio, which may hinder proper hydration and negatively affect the microstructure of the concrete. These findings highlight the importance of optimizing MRWR content to achieve the desired balance between early-age strength and long-term strength development.

The results of this study demonstrate that the HSC, utilizing river gravel residue as a substitute for traditional coarse aggregate (limestone), combined with HC and FA as a binder, can be produced with the incorporation of MRWR (the combination of Type D and Type G). Type D acts as a water-reducing and set-retarding agent, while Type G provides high-range water reduction with similar set-retarding properties. However, using excessive amounts of MRWR can lead to an excessively low water content in the concrete mix, which subsequently impairs the hydration reactions of both HC and FA. This reduced hydration activity negatively impacts the development of compressive strength over time (Jia & Wang, 2022; Ammar et al., 2024).

In addition, excessive use of MRWR can disrupt the delicate balance between water reduction and concrete workability. While reducing water content generally improves early compressive strength, overuse of MRWR can lead to the mix becoming too dry or cause uneven dispersion of cement particles. This negatively impacts the hydration process, ultimately hindering the development of compressive strength (Dong et al., 2020; Al Haffar et al., 2021). Based on these observations, the optimal MRWR dosage for enhancing the compressive strength of HSC under the tested conditions should not exceed 1.5%. This dosage maintains a balance between compressive strength improvement and workability without compromising the mechanical properties of the concrete.

3.2 Role of river gravel residue in enhancing concrete performance

Fig. 6(a) shows the naturally rounded shape and smooth surface of river gravel residue, which allows for better rolling and flow during mixing, hence facilitating the uniform dispersion of binder within the cement paste. This uniformity leads to a more efficient and consistent hydration process, ultimately contributing to the steady development of compressive strength throughout the curing period. Additionally, the smooth surface of river gravel has a direct impact on the behavior of the interfacial transition zone (ITZ), which serves as the boundary between the cement hydration products and the aggregates. As highlighted by Lyu et al. (2019), the surface texture of aggregates can significantly affect both the porosity and the continuity of the ITZ. This observation helps explain why the surface condition of aggregates, even when smooth, still plays a meaningful role in the microstructural development of concrete.

(a) River gravel residue and (b) Failure of concrete specimens.
Fig. 6.
(a) River gravel residue and (b) Failure of concrete specimens.

Meanwhile, Alanazi et al. (2022) reported that hydration products within the ITZ strongly influence the overall strength of concrete. Although the smooth surface of river gravel may reduce mechanical interlocking, the uniform dispersion of binder, together with the use of MRWR, enables a lower w/b ratio while maintaining good workability. The result leads to a denser cement paste, reduced porosity and discontinuity in the ITZ, and promotes the continuous formation of C–S–H around the gravel surface. These observations are consistent with the findings of Li et al. (2012), who demonstrated that effective improvement of the ITZ is directly associated with the development of compressive strength over curing time. Therefore, under appropriate proportions of HC, FA, and MRWR, this mechanism supports the formation of a dense microstructure and the continuous development of strength in concrete throughout the curing period.

In addition to enhancing the concrete’s mechanical properties, river gravel residue offers environmental benefits. By minimizing the need for energy-intensive extraction processes associated with quarrying traditional aggregates, using river gravel residue reduces the overall consumption of energy and resources. This makes river gravel residue a more sustainable and eco-friendly alternative, aligning with the construction industry’s ongoing efforts to mitigate environmental impacts.

The interparticle bond plays a vital role in increasing concrete strength over time (Schneider et al., 2011; Prusty et al., 2016). While river gravel residue has a smooth, rounded surface, using a suitable binder and MRWR can improve its performance. This strategy ensures adequate adhesion between the cement paste and aggregates, which helps in achieving the desired compressive strength. Fig. 6(b) illustrates the failure pattern of concrete specimens under compressive load. The failure develops within the cement paste and shears along the surface of the river gravel residue. These observations confirm that river gravel residue is an effective coarse aggregate for producing HSC, meeting the 60 MPa design target. Moreover, they demonstrate that river gravel residue works well with HC and FA.

Importantly, river gravel residue also improves the workability of concrete, even when using low w/b ratios. The addition of river gravel residue facilitates better flowability of the concrete, enhancing the workability of the mixture while reducing the water content. This leads to denser concrete, which is essential for achieving both higher compressive strength and long-term durability. The ability of river gravel residue to maintain good workability at low w/b ratios makes it particularly advantageous in the production of high-performance and sustainable concrete.

3.3 Temperature of chemical reaction

Fig. 7 illustrates the temperature variations within cement paste containing varying percentages of FA replacement at different curing times. The purpose of monitoring temperature variations was to better understand the chemical mechanisms associated with increasing FA content. Specifically, the objective was to examine whether FA influences the activation of the hydration process or alters the formation of hydration products. Such measurements are important because they reflect the rate of chemical reactions and the associated heat release, both of which are directly linked to the development of compressive strength and the microstructural evolution of concrete. This approach underscores the connection between chemical behavior and mechanical performance, while also providing a means to evaluate the role of pozzolanic materials and admixtures in enhancing overall concrete performance. FA replacement at levels between 10% and 20% leads to an increase in the internal temperature of the cement paste across all curing ages. This rise in temperature occurs due to the hydration reaction between cement and water, which produces C-S-H and Ca(OH)2. This process generates heat, with calcium oxide present in FA accelerating the hydration reaction, resulting in an overall increase in the internal temperature of the mixture.

Temperature change of cement paste at different FA contents.
Fig. 7.
Temperature change of cement paste at different FA contents.

The results demonstrated that the maximum recorded temperature remained below the engineering threshold of approximately 70°C. This limit is generally recommended to prevent delayed ettringite formation and to reduce the risk of thermal cracking (Giatec Scientific Inc., 2020). In addition, the measured temperature differential (ΔT) within the concrete mass did not exceed 20-25°C. This range is considered safe to avoid thermally induced stresses that could otherwise lead to structural cracking (National Ready Mixed Concrete Association [NRMCA], 2020). These findings confirm that the hydration process in this study posed no risk of thermal cracking. More importantly, they highlight the role of FA in modifying hydration mechanisms. This agrees with previous studies that have established correlations between time–temperature profiles and the strength and durability of high-performance and mass concrete (El-Mir, Assaad, Nehme, & El-Hassan, 2022). Prior work has also addressed the influence of coarse aggregates on hydration heat-release behavior (Tan et al., 2024). The temperature trends observed here are consistent with the long-term development of compressive strength in mixtures incorporating FA. This further validates the beneficial role of FA in sustainable HSC.

Moreover, the silicon dioxide (SiO₂) present in FA reacts with Ca(OH)2, which is a by-product of the cement hydration, to produce C-S-H further, contributing to the continuous heat generation throughout the hydration process (Bourchy et al., 2020; Chai et al., 2021). These compounds play a crucial role in enhancing the hydration process, particularly in cases where the w/b ratio is low, as in the case of HCFA20 (w/b = 0.308). Under such a condition, the hydration reaction intensifies, resulting in greater heat generation. The limited water content allows the chemical components in HC and FA to react more efficiently and intensively, thereby increasing the heat released during the entire curing period (Chai et al., 2021; Ding et al., 2024).

This finding is consistent with the study by Hu et al. (2014), which affirmed that a low water-to-cement (w/c) ratio accelerates the release of heat from hydration reactions, particularly during the initial hours. However, the rate of hydration decreases thereafter. HCFA30 exhibits a reduction in internal temperature compared to HCFA20, while HCFA10 consistently demonstrates the lowest internal temperature across most curing periods. Although FA contributes additional calcium oxide (CaO) and silicon dioxide (SiO₂) to the binder matrix, the significantly low w/b ratio may result in insufficient water for the hydration reaction to proceed completely. This deficiency leads to a reduction in heat generation (Sun et al., 2019; Ding et al., 2024; Huang et al., 2024), which in turn impacts the development of compressive strength.

The test results reveal that the compressive strength of HCFA30 is lower as compared to that of HCFA20, indicating that the primary cause is the high replacement level of HC with FA at 30%. This high FA content significantly reduces the amount of cement, which is the primary binder contributing directly to strength development. Although the inclusion of FA introduces additional CaO and SiO₂ into the binder matrix, the excessive replacement level also results in the predominance of the pozzolanic reaction, which proceeds at a slower rate compared to the cement hydration. This slower reaction cannot fully compensate for the reduction in HC content within the specified curing period. Furthermore, a low w/b ratio may limit the availability of water sufficient for the hydration of both HC and FA, leading to incomplete reactions and reduced strength development. In addition, it is plausible that a portion of the available water is consumed in reactions with FA. Consequently, incorporating a very high FA content (30%) may result in inadequate water availability for the hydration process, leading to incomplete hydration reactions and a corresponding reduction in compressive strength (Chai et al., 2021; Huang et al., 2024).

Fig. 8 demonstrates the temperature variation in cement paste incorporating a 20% FA replacement (HCFA20), with varying dosages of MRWR at 1%, 1.5%, 3%, 4.5%, and 6%. Increasing the MRWR dosage from 1% to 1.5% significantly enhances the heat released during the hydration process. This increase in heat generation is attributed to the improved dispersion of cementitious materials, which facilitates more efficient hydration. At the 1.5% dosage level, the cement paste recorded the highest average temperature of 31.3°C (±0.90°C), compared to 30.0°C (±0.98°C) at the 1% dosage. This finding suggests that the hydration process at the 1.5% dosage is more complete and results in a higher rate of exothermic reaction during early hydration (Wu et al., 1983; Poon et al., 1999; Gong et al., 2020). However, as the dosage of MRWR increases beyond 1.5%, the average temperature begins to decline. Specifically, at dosages of 3%, 4.5%, and 6%, the temperatures drop to 29.5°C (±0.82°C), 29.5°C (±0.79°C), and 29.3°C (±0.82°C), respectively. This decline is indicative of reduced hydration activity, likely due to the excess MRWR causing a delay in the cement setting process.

Temperature change of HCFA20 cement paste at different admixture contents.
Fig. 8.
Temperature change of HCFA20 cement paste at different admixture contents.

The retardation effect of the MRWR appears to surpass its hydration acceleration benefits when the dosage exceeds 1.5%, leading to a decline in compressive strength development. The 1.5% dosage represents the optimal balance between improving hydration and achieving compressive strength. In contrast, higher dosages disrupt the hydration process, leading to incomplete hydration and lower heat evolution, ultimately resulting in reduced strength gain. This observation aligns with the findings of Mitchell & Margeson (2006), who demonstrated that the curing temperature directly influences the efficiency of set-retarding admixtures. Their study reported that at higher curing temperatures (40°C), retarders delayed the setting by approximately 5 h, whereas at lower temperatures (25°C), the delay extended to 20 h, further influencing the hydration kinetics (Feng et al., 2020; Kim et al., 2022; Huang et al., 2024).

4. Microstructural Analysis

Figs. 9(a and b) illustrate high-magnification images (100X) and the chemical composition analyses of specimens, in which HC was partially substituted with 20% FA (HCFA20). These analyses were conducted on specimens cured for 14 and 28 days, respectively. The results from SEM and EDS consistently demonstrate similar trends in particle distribution and microstructural development across both curing ages. At a 1% dosage of MRWR, the structure exhibits pronounced voids and interconnected porosity, indicating insufficient material densification. Although C-S-H gels are generated as a hydration product, their formation is insufficient to fully occupy the void spaces. This inadequacy disrupts the homogeneity of the particle matrix, resulting in residual porosity within the microstructure. Consequently, the material demonstrates reduced compressive strength when compared to specimens incorporating an optimal admixture dosage (Mehta & Monteiro, 2014). This observation aligns with the findings of Yu et al. (2024), who reported that uneven particle distribution and insufficient material densification are typically attributed to the inadequate formation of C-S-H gels. These deficiencies hinder the complete filling of void spaces within the microstructure, resulting in pronounced porosity that significantly compromises the structural integrity (Yu et al., 2024).

(a-b) SEM and EDS analysis results of HCFA20 specimens with various MRWR contents.
Fig. 9.
(a-b) SEM and EDS analysis results of HCFA20 specimens with various MRWR contents.

Increasing the dosage of MRWR to 1.5% results in a noticeably denser microstructure, which is characterized by a more uniform distribution of particles. This improvement is primarily due to the enhanced formation of C-S-H gels, which effectively fill void spaces within the structure. As a consequence, porosity is significantly reduced, and the compressive strength reaches its highest level.

At a 3% dosage of MRWR, the particle distribution and C-S-H gel formation become irregular, with localized agglomeration observed in certain areas. This phenomenon can be attributed to the excessive MRWR dosage, which causes particle segregation and clustering. Consequently, voids are generated in specific regions and occasionally form interconnected pores along continuous paths. These irregularities lead to a reduction in structural density compared to the 1.5% dosage level. Exceeding the optimal MRWR dosage disrupts the balance necessary for uniform gel formation, resulting in uneven C-S-H distribution and increased porosity.

Fig. 10 illustrates the results of the XRD analysis, which reveals that at a MRWR content of 1%, a high calcium concentration was observed, indicating a significant formation of Portlandite (Ca(OH)₂). The elevated Portlandite content suggests insufficient production of C-S-H gel, which is critical for filling voids between particles. This deficiency results in a porous and low-density microstructure. These findings align with the SEM images, which show voids within the microstructure, reflecting incomplete particle distribution and inadequate density. Consequently, this limits the compressive strength enhancement of the material (Moghaddam et al., 2019).

XRD analysis results of HCFA20 specimens with various MRWR contents.
Fig. 10.
XRD analysis results of HCFA20 specimens with various MRWR contents.

At 1.5% MRWR content, the EDS analysis indicates an increase in silicon and a decrease in calcium compared to the sample with 1% MRWR content. This shift reflects a higher formation of C-S-H gel, which effectively fills voids within the structure, resulting in a denser microstructure with reduced porosity and improved particle uniformity. These changes align with the SEM images, which reveal a more compact and uniform microstructure. The incorporation of FA further promotes the intensified formation of C-S-H gel, reducing the residual Portlandite content (Branch et al., 2016). At 3% MRWR content, the EDS analysis reveals a significant decrease in silicon and a marked increase in calcium and carbon concentrations. This indicates excessive accumulation of Portlandite, which fails to adequately react with silicon to form sufficient C-S-H gel due to the overly high additive content. This imbalance leads to an uneven distribution of C-S-H gel within the structure, resulting in localized particle agglomeration. These findings are consistent with the SEM images, which show an irregular microstructure with porosity in certain areas. The uneven particle distribution and localized porosity may reduce the overall density of the structure, increasing its susceptibility to segregation and long-term water and chemical ingress (Bae et al., 2014).

The compressive strength testing and microstructure analysis demonstrate clear consistency, indicating that HC, FA, and MRWR work effectively together. The combination of these materials significantly enhances the mechanical properties and improves the microstructure of the concrete. FA plays a crucial role as a filler, reducing voids and promoting pozzolanic reaction. Simultaneously, the MRWR improves the dispersion of cementitious particles, reduces water content in the mix, and contributes to a denser and stronger concrete structure. Overall, the combination of these materials and river gravel residue with the suitable formula results in high-performance concrete that is both environmentally friendly and resistant to harsh conditions, making it suitable for construction projects requiring high strength and long-term sustainability.

Recent findings by Kannur and Chore (2022; 2023) highlight the critical role of pozzolanic materials in improving the microstructural and durability performance of concrete. Their studies demonstrated that the incorporation of pozzolanic materials significantly reduces the amount of Ca(OH)₂, a by-product of Portland cement hydration. The reduction of Ca(OH)₂ not only mitigates the alkalinity that may accelerate steel reinforcement corrosion but also promotes the formation of C–S–H, which enhances the strength and stability of the cementitious matrix. In addition, pozzolanic reactions facilitate the development of alumino-silicate gels (C–A–S–H), which decrease porosity and increase the overall density of the structure. FTIR analyses further confirmed the formation of new Si–O–Si and Al–O–Si bonds, characteristic of C–S–H and C–A–S–H gels. These molecular-level transformations are directly associated with reduced water absorption and chloride penetration, thereby improving the long-term durability of concrete under aggressive environmental conditions.

The XRD, SEM, and EDS results of this study further confirm the reduction of Ca(OH)₂ and the enhanced formation of C–S–H and C–A–S–H gels within the ITZ. These findings are consistent with previous reports on concretes incorporating pozzolanic materials, where pozzolanic reactions were shown to consume CH and generate new Si–O–Si and Al–O–Si bonds. Such microstructural refinements lead to reduced porosity, lower water absorption, and improved resistance to chloride penetration, thereby ensuring enhanced long-term durability (Kannur & Chore, 2021; 2023a; 2023c; 2024; 2025b).

5. Conclusions

This study focuses on assessing the feasibility of producing HSC using HC as the primary binder and FA as a supplementary binder. The MRWR (combined Types D and G) was selected to enhance the dispersion of binders and optimize the concrete’s compressive strength instead of expensive high-range water-reducing admixtures. The findings of this study are summarized as follows:

  • 1.

    The production of HSC using FA and HC demonstrated significant potential for reducing CO₂ emissions from cement production, thereby mitigating environmental impact. This approach addressed the growing need for sustainable practices in the construction industry and is highly compatible with the Sustainable Development Goals of Thailand.

  • 2.

    The replacement of HC with 20% FA, combined with 1.5% MRWR, was identified as an optimal ingredient for effectively enhancing the compressive strength of HSC. However, exceeding these proportions of FA and MRWR negatively affected the hydration process, resulting in a reduction in compressive strength.

  • 3.

    The MRWR content directly influenced the microstructure and compressive strength of HSC. An MRWR level of 1.5% was identified as the optimal dosage, as it significantly enhanced the microstructural density by reducing porosity and ensuring uniform dispersion of C-S-H gel. This optimal combination resulted in the highest compressive strength. Conversely, excessive MRWR content caused particle segregation and agglomeration, which led to increased porosity and reduced density and compressive strength.

  • 4.

    The use of river gravel residue in concrete has shown considerable potential as a sustainable alternative to traditional coarse aggregates. Its naturally rounded shape and smooth surface improved the workability of the mix, facilitating better uniformity during mixing. Furthermore, river gravel residue supports environmental sustainability by reducing dependency on quarried stone, decreasing energy consumption in material production, and encouraging the use of locally sourced resources. These attributes make river gravel residue a valuable component for promoting sustainable construction practices.

Acknowledgements

The authors acknowledge the support from Uttaradit Rajabhat University and Suranaree University of Technology.

CRediT authorship contribution statement

Aroondet Boonsung: Conceptualization, methodology, investigation, validation, formal analysis, writing – original draft, writing – review & editing, supervision, project administration. Suksun Horpibulsuk: Writing – review & editing, visualization, supervision, resources, project administration, formal analysis, conceptualization. Jitwadee Horpibulsuk: Visualization, validation, formal analysis. Arul Arulrajah: Writing – review & editing, visualization.

Declaration of competing interest

The authors declare that they have no competing financial interests or personal relationships that could have influenced the work presented in this paper.

Data availability

Data will be made available on reasonable request.

Declaration of generative AI and AI-assisted technologies in the writing process

The authors confirm that there was no use of artificial intelligence (AI)-assisted technology for assisting in the writing or editing of the manuscript and no images were manipulated using AI.

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