The cement and plastic materials found to be a product of routine life which means the cement is required for the development of infrastructure (Li et al., 2023[1]), while the plastic is being used as a carry bag, wrapping product, food packaging etc. These materials are the prime factors which are responsible for the development of the nation and to make life very easy for each of us. On the other hand, several risks are also associated with the usage of these materials i.e. due to very fine suspended particles of cement dust which may affect the human health by entering in the body through air and the nanoparticles of plastic contaminated the drinkable water and ultimately affect the human body i.e. as the nanoparticles of plastic entered in the human body through several ways, Gigault et al. (2018) [2]. Beside this, manufacturing of cement and the plastic bags exerts several gases into the environment (19–20% of CO2 produced during the cement manufacturing) which are the real threat to the environment. It is to note that different types of chemicals (i.e. around 8000) are supposed to be used in the manufacturing of the plastic which have more hazardous effects on the environment as well as on the human health in comparison to the CO2, Wiesinger et al. (2021) [3]. Therefore, in order to preserve the natural resources and to create a sustainable environment, there is a need to propose some guidelines regarding the usage of these waste materials in different construction practices which may result in the sustainable environment, Gencel et al. (2021) [4]. Steel industry has become the one of the most important industries in the world which is responsible for producing waste material i.e. slag along with the production of raw materials, Santhosh et al., (2021) [5]. Due to the production of slag on a large scale, there are a lot of opportunities for the construction sector to utilize the slag in sustainable construction practices and help in reducing the environmental pollution, Lu et al., (2023) [6]. As per the report of Indian Bureau of mines (2015) [7], production of cement in India is booming by 10% annually. While, Mehraj et al (2013) [8] stated that the increment in the quantity of suspended cement dust particles in an open environment results in the increase in several diseases like skin related, heart disease and many more which may affect the quality of life. Boora and Dharma (2022) [9] stated that the several non-treatable diseases like chronic respiratory diseases, asthma, and chronic obstructive pulmonary which are responsible for 10.7% deaths out of 82% total deaths happening due to the entering of these suspended dust particles into the human body. Another important reason to focus on the application of industrial byproducts is because of scarcity of their dumping in an open landfill which contaminates the soil mass as well as reduces the land fertility, Vishwakarma and Uthaman (2019) [10]. Due to this alarming situation, there is a need to utilize different waste materials in different construction practices which may help in creating a sustainable environment and preserving the natural resources.
Concrete is a mixture of cement, fine aggregate, coarse aggregate and water. Therefore, steel slag could be utilized as the replacement of coarse or fine aggregate in the concrete. Earlier, an experimental study was conducted by focusing on the application of slag as the replacement of fine aggregate in order to check its impact on the mechanical properties of concrete mix, Teng et al. (2013) [11]. On the basis of the findings it was observed that the slag is a beneficial product as the replacement of sand as it speeds up the hydration process along with the increment in the early age strength. Earlier, Qasrawi et al., (2009) [12] reported reduction in the workability of the concrete mix due to the incorporation of steel slag as the replacement of fine and coarse aggregate. Though, the rate of decrease in the workability was found to be at the lower side. While in case of PA as the replacement of coarse aggregate, the workability was found to be increased due to the lower water absorption capability of PA. Choi et al. (2005) [13] reported an increase in the workability of PET bottles lightweight aggregate concrete (WPLAC) due to the inclusion of plastic aggregate as the replacement of coarse aggregates. The main reason was the availability of the extra water i.e. plastic aggregate water absorption capacity is very low. Azhdarpour et al. (2016) [14] observed that the inclusion of PET aggregates (i.e. up to 10%) having a size of 2–4.9 mm as coarse and 0.05–2 mm as fine aggregate increased compressive and flexural strength.
Devi and Gnanavel (2014) [15] examined the effect of steel slag on the workability of concrete mix. Based on the results, reduction of 20% in the workability was reported after the use of 30% steel slag as the replacement of coarse aggregates. Although, Monosi et al. (2016) [16] reported that the reduction in workability was overcome with the use of plasticizer and improved mechanical properties for concrete mix. It was recommended to utilize the EAFS after proper crushing to ensure the proper grading. It was also concluded that the use of EAFS as coarse aggregate could achieve higher strength in comparison to mixes containing natural coarse aggregate alone. Several other studies also recommended the use of steel slag as a replacement for aggregate due to the improvement in tensile strength and shrinkage properties of concrete mix, Rondi et al. (2016) [17]. The use of EAFS was recommended due to its ability to reduce the shrinkage problem in concrete mix as well as volume expansion characteristics of EAFS, Santamaría et al. (2018) [18]. Besides, it was also observed that the use of slag helps in reducing the cement content in mix for the required strength. Fronek et al. (2012) [19] concluded that the slag becomes no expansive after processing it. An observation was made that incorporating treated slag in concrete mixture resulted in the attainment of the highest strength after a 28-day curing period, surpassing the strength achieved by using untreated or as-received slag. This improvement is attributed to the enhanced cementitious behavior of the slag, which occurs only after undergoing reprocessing, Muhmood et al. (2009) [20]. The use of copper slag upto 40% was recommended as a replacement of fine aggregate, beyond which increased number of voids may occur which led to the failure, Wu et al. (2010) [21]. Pellegrino and Faleschini (2013) [22] concluded that the EAFS may be used as 100% replacement of coarse aggregate which will be beneficial from economical as well as environmental point of view. However, Pellegrino et al. (2013) [23] stated that the coarse aggregate was replaced with steel slag up to a maximum proportion of 50% without affecting the mechanical properties of the mix.
Based on the detailed literature review, it was observed that most of the studies reported the use of slag as a partial replacement of fine and coarse aggregate. A limited number of studies were found heretofore to use as partial replacement of slag with cement and FA. Also, the performance of plastic aggregate along with the steel slag found to be limited. Therefore, the present study is focused on a sustainable environment by minimizing the depletion of natural resources such as river sand and coarse aggregate and reducing CO2 emissions by reducing the cement usage in the concrete production. Hence, the optimization of the mix design was performed by replacing the cementitious slag up to 50% (0, 10, 20, 30, 40 and 50%) of cement whereas fine slag aggregate replaced upto 70% 0, 10, 20, 30, 40, 50, 60 and 70%) of river sand, see Section 2. Further, the optimization of the design was performed by replacing the plastic aggregate up to 50% (0, 10, 20, 30, 40 and 50%) of coarse aggregate, see Section 2. The optimized mix is proposed based on the tests on fresh concrete and hardened concrete, see Section 3. Based on the optimization, the cement and fine aggregate both in combination were replaced by the steel slag whereas the coarse aggregate is replaced by the plastic aggregate and studied against compression, flexure and tension tests, see Section 4. Further, SEM, energy dispersive X-ray (EDS) was performed to identify the types and the quantity of elements present in a concrete whereas the X-ray diffraction analysis was performed in order to examine the crystallographic structure of a material, see Section 5. The major findings are elaborated and presented at Section 6.