1. Introduction
Clay is one of the oldest construction materials and clay bricks has been extensively used in the construction industry. The use of clay bricks to build adobe houses dates back to 8000 BC [
1,
2]. In Pakistan, conventional burnt clay bricks are widely used in the construction industry. Pakistan is the third largest country in South Asia, producing about 45 billion burnt clay bricks per year. In Pakistan, approximately 18,000 brick kilns are functional of which about 7966 brick kilns are functional in Punjab, Pakistan [
3,
4,
5].
The various steps involved in brick preparation are screening of clay to remove debris; manual mixing of clay, sand, and water to make a homogenous mix; molding of brick into the desired shape and size; the drying of brick in the open air; burning of brick in brick kilns at temperatures ranging between 850 and 950 °C to achieve the required hardness, color, and strength [
6,
7,
8]. The production of burnt clay bricks involves the use of beneficial clayey soil, which is important for the cultivation of valuable crops [
9,
10,
11]. In addition, the production of conventional burnt clay bricks releases harmful gases such as carbon dioxide (CO
2), carbon monoxide (CO), and sulfur dioxide (SO
2) into the environment, enhancing air pollution and negatively affecting human health and the economy [
12]. CO
2 is one of the main sources of greenhouse gases (GHG), which causes global warming [
13,
14,
15]. Moreover, sulfur dioxide (SO
2) and other carcinogenic dioxides and particulate matters (PM) released from the brick kilns have a negative impact on human health [
16,
17].
In Pakistan, particularly in metropolitan cities, the smog which is a combination of smoke and fog descends in the winter season. Smog has severe negative socio-economic impacts. Airports, motorways, and highways are required to be closed at night and early morning due to smog, which results in delays in the movement of transport goods and the public. Smog has a detrimental impact on the health of the people living in these metropolitan cities, which over burdens the government hospitals in these cities. In the winter season, brick kilns are shut down to reduce the negative impact of smog, which results in reduced production of burnt clay bricks and slowing down of the construction projects [
18]. In China and India, the use of clay bricks in the construction work has been reduced to limit the excavation of top fertile clayey soil and to reduce the CO
2 and other GHG emissions [
19,
20,
21].
Coal ash (CA) is produced in huge amounts (0.16 billion tons per year) all over the world. However, CA has limited use in the construction industry, mainly in the cement industry [
22,
23]. CA is an industrial by-product obtained from coal power plants (CPP). In Pakistan, nine CPPs are functional and are producing large amounts of CA. The CA obtained from these CPP is pozzolanic in nature and can be used as a partial replacement for clay in the manufacturing of bricks [
24,
25,
26]. The CA primarily comprises silicon dioxide (SiO
2), alumina oxide (Al
2O
3), and iron oxide (Fe
2O
3), these oxides react with the calcium oxide in clay and form calcium alumino silicate hydrate (C-A-S-H) and calcium silicate hydrate (CSH) gels. These gels provide the required strength for the CA concrete mix [
27].
The use of CA in the brick industry has substantially increased over the years. To reduce the use of clayey soil in burnt clay bricks and to reduce the CO
2 emissions in the manufacturing of clay bricks, CA bricks have emerged as an environmentally friendly and cost-effective alternative to clay bricks. CA bricks are lightweight bricks with reduced thermal conductivity, lower water absorption, and improved durability compared with conventional burnt clay bricks [
28,
29]. CA bricks have up to 10% lesser weight than conventional burnt clay bricks [
30,
31]. CA bricks also reduce the landfill sites needed to dispose of waste CA [
32,
33].
In the available research investigations, numerous studies used lime and cement to produce CA bricks [
34,
35,
36]. The lime and cement, rich in calcium oxide, react with silicon dioxide and alumina oxide in CA forming calcium silicate hydrate (C-A-S-H) gel, which develops the strength in CA bricks [
27]. In general, gypsum and lime are commonly used in CA bricks to significantly enhance the compressive strength [
37]. Prasad et al. [
38] developed CA bricks by using calcium-gypsum (Cal-g) with varying percentages of fine aggregates and stone. The test results indicated that the mix with a water to Cal-g ratio of 0.2 attained the compressive strength of 9.14 MPa [
38]. Turgut et al. [
39] investigated the influence of varying lime content on the compressive strength of CA bricks. The 28-day compressive strength of CA bricks with 10%, 20%, and 30% replacement of lime with CA resulted in 14 MPa, 15 MPa, and 18 MPa compressive strength, respectively [
39]. Chindaprasirt et al. [
30] investigated the influence of varying percentage replacement levels of CA with hydrated lime on the compressive strength of CA bricks. The compressive strength of CA bricks was increased by 18% (51 MPa to 62.5 MPa) as the percentage replacement of lime with CA was increased from 5% to 10% [
30]. Moghaddam et al. [
40] investigated the influence of six varying particle sizes of CA. The study noted that the compressive strength was increased with increasing percentage fineness of CA due to the increased formation of needle shape crystalline structures in C-A-S-H gel [
40].
In recent years, CA bricks prepared with lime made way for CA bricks prepared with cement. CA bricks prepared with cement require no special curing treatment. CA bricks prepared with a blend of sand and cement are the major step toward the production of eco-friendly durable bricks [
20,
36,
41]. Sivakumar et al. [
42] investigated the influence of cement content on self-compacted CA bricks comprising bottom CA, fly CA, and cement. The study noted that the optimum compressive strength of 17.4 MPa was achieved using a bottom CA, fly CA, and cement ratio of 1.25:1:0.45 [
42]. Wang et al. [
43] prepared CA bricks by applying forming pressure. The optimum compressive strength of 18.4 MPa was achieved with 63% CA, 15% gravel, 10% cement, and 12% sand [
43]. Alam et al. [
44] investigated the CA brick tiles comprising CA, fine sand, coarse sand, and cement. The optimum compressive strength of 4.5 MPa was achieved using a CA:fine sand:coarse sand:cement ratio of 70:15:5:10 [
44].
Although the use of cement increases the compressive strength of CA bricks, the disadvantage of using cement in CA bricks is the increasing cost of CA brick. Hence, it is important to determine the optimized dosage of cement in CA bricks for the large-scale production of CA bricks. In Pakistan, numerous CPPs built under the China Pakistan Economic Corridor are operational, which are producing CA as industrial waste, and CA needs to be removed from the CPP sites for the continuous and effective running of these CPPs. The use of CA as a replacement for clay in bricks is a major step toward the production of environmentally friendly and cost-effective CA bricks as dumping CA in landfills is a hazardous and impractical solution. In addition, CA bricks will preserve the fertile clayey soil. This research investigates various physical and mechanical properties of CA bricks. The influence of the leaching effect on CA bricks is beyond the scope of this paper.
2. Experimental Program
The experimental program was designed to investigate the influences of cement content, sand content, quarry dust content, and duration of application of forming pressure on the various physical and mechanical properties of unburnt CA bricks. The cement contents, sand, and quarry dust contents were selected based on an extensive review of the literature [
43,
44,
45]. A total of six unburnt CA brick mixes were prepared. Mix 1 and Mix 2 comprise 60% CA, 10% lime, 5% cement, 15% sand and 10% quarry dust by weight. Mix 3 and Mix 4 comprise 60% CA, 10% lime, 10% cement, 10% sand, and 10% quarry dust by weight. Mix 5 and Mix 6 comprise 60% CA, 10% lime, 15% cement, 10% sand and 5% quarry dust by weight. In all the mixes, the water to binder ratio was 0.25. The unburnt CA bricks in Mix 1, Mix 3, and Mix 5 were subjected to a forming pressure of 29 MPa for 3 s whereas the unburnt CA bricks in Mix 2, Mix 4, and Mix 6 were subjected to a forming pressure of 29 MPa for 6 s (
Table 1).
The unburnt CA bricks were prepared in four steps. In the first step, the required quantities of CA, cement, lime, sand, quarry dust, and water contents were weighed in the digital weighing balance. In the second step, all the weighed contents in the designed mix proportion were added to the concrete mixer to prepare a homogenous mix as per ASTM D6103-17e [
46]. In the third step, the mix was poured into the brick molds in three layers. Each layer was properly compacted to minimize the air voids in the brick specimens. In the fourth step, the brick specimens were subjected to the forming pressure of 29 MPa for either 3 s or 6 s (
Figure 1). A total of 240 CA bricks of 230 mm length, 114 mm width, and 70 mm thickness were cast. CA bricks were moist cured for 28 days.
6. Conclusions
In this experimental study, six coal ash (CA) brick mixes with CA content (60%), lime content (10%) and varying cement contents (5%, 10%, and 15%), sand contents (10% and 15%), and quarry dust contents (5% and 10%) subjected to the forming pressure of 29 MPa for either 3 s or 6 s were prepared. The various physical (weight per unit area, water absorption, efflorescence, soundness) and mechanical (compressive strength, modulus of rupture) tests were conducted on sustainable unburnt CA bricks. The following conclusions are drawn based on the test results presented in this research work.
The weight per unit area of CA bricks prepared with forming pressure applied for 6 s was about 4% higher than those of CA bricks prepared with forming pressure applied for 3 s. The average weight per unit area of CA bricks (11 g/cm2) was 31% lower than that of conventional clay bricks (15–17 g/cm2).
The experimental results exhibited that the percentage of water absorption of CA bricks (6–11%) was significantly lower than the percentage of water absorption of conventional clay bricks for severe weather resistance bricks (17%) and moderate weather resistance (22%).
CA bricks exhibited higher compressive strengths than conventional clay bricks. CA bricks with 60% CA, 10% lime, 10% cement, 10% sand, and 10% quarry dust exhibited the optimum average compressive strength of 19 MPa, which was greater than the minimum compressive strength limits of clay bricks as per Pakistan Building Code 2021 [
8] (8.5 MPa) and BS 3921-04 [
67] (13.8 MPa)
CA bricks with 60% CA, 10% lime, 10% cement, 10% sand, and 10% quarry dust exhibited the optimum modulus of rupture of 2.10 MPa, which was greater than the minimum modulus of rupture limit of clay bricks (0.65 MPa) as specified in ASTM C67-20 [
61].
CA bricks with 5% cement content exhibited minimal efflorescence; however, CA bricks with 10% and 15% cement contents exhibited no efflorescence. This is the major advantage of CA bricks as conventional clay bricks exhibit significant efflorescence.
The CA bricks with 5% and 10% cement contents are 25% and 10% cheaper than the conventional clay bricks.
The unburnt CA bricks developed in this study are cost-effective and a sustainable alternative to conventional burnt clay bricks.