The construction and building material market remains dominated by concrete to this day, after becoming widely used since the turn of the 20^th century [1]. Throughout most of the world, concrete is made using Portland cement as the major ingredient. During the past 20 years, Portland cement production has increased by three times (from 1.10 to 3.27 billion tons). In 2030, the expansion of the construction industry will lead to a staggering 4,83 billion tonnes of cement being produced [2]. In consequence, concrete production will increase, requiring an increase in natural aggregate (NA) consumption, including fine and coarse aggregates, since the NA constitutes 60-75% of concrete production. According to estimates, NA consumption reached 48.3 billion tonnes in 2015 and has grown at a rate of more than 5% every five years [3]. The current growth rates are expected to lead to a doubling of NA demand within 20 to 30 years [4]. The use of recycled aggregate (RA) from construction and demolition waste (CDW) can therefore conserve NA resources, reduce landfill demands, and contribute to a more sustainable built environment. Concrete produced by this process is referred to as RA concrete (RAC).

Following World War II, demolition waste from construction was used to produce the first RAC. The bombardment of German and English cities during that time generated a tremendous amount of rubble and debris [5]. Globally, 40 billion tons of aggregate grain are produced as a result of a large number of development projects being undertaken throughout the world [6]. The CDW consists of metal, concrete, minerals, and wood, as well as other unsorted fractions and miscellaneous waste. In the last 25 years, RAC has been extensively studied for its mechanical properties, durability, and structural performance. In general, the process of designing concrete mixes for RAC is the same as that used in conventional concrete [7]. A notable characteristic of recycled concrete aggregate (RCA) is that it is extremely water-absorbing, and therefore, it requires more water to be mixed into concrete. Additionally, Poon et al. [8] used scanning electron microscopy to examine the interfacial zone of RAC and conventional concrete. Their results showed that RAC contained predominantly loose and porous hydrate compositions, whereas conventional concrete consisted of dense hydrate compositions. Tam et al. [9] and Etxeberria [10] concluded that RAC microstructures were for the most part more complex than conventional concrete microstructures. RAC has two interfacial transition zones (ITZs): (i) one located between the old mortar matrix and the attached to the RCA (the former ITZ), and (ii) one located between the new mortar matrix and the RCA. RAC is susceptible to failure due to a weak link caused by the porous and cracked mortar.

According to several research reports [11-13], RAC has a significantly lower elasticity modulus than conventional concrete (ranging between 15 and 45%). In general, with increasing RA content in RAC, its compressive strength will decrease [14-17]. The uniaxial compressive strength also decreases with an increase in RCA content [18]. In comparison with concrete produced with natural aggregates, RAC has approximately 81% compressive strength [19]. The low density in the transition zone between paste and aggregate plays a major role in the reduction of strength in RCA, but there are other characteristics of the recycled material that also contribute to this reduction [13]. Through the use of RCA, concrete properties can be improved in several ways, the most significant of which is the adoption of an extended curing cycle and the use of pozzolanic materials combined with an altered water-cement ratio [20]. Moreover, RAC concrete and conventional concrete provide comparable results in terms of uniaxial tensile strength [21]. In the study conducted by Li et al. [14], the researchers demonstrated that when mixing concrete, the proportions of cement and water can be adjusted fairly precisely to accomplish the targetted compressive strength (CS). This finding was corroborated by Buck's [22] experiments, which also demonstrated that RAC could be made stronger than the parent concrete that yields the RCA. Although RAC has a higher chloride ion permeability than conventional concrete [23], it still retains an acceptable resistance to chloride ion penetration [24, 25]. In the RAC, drying shrinkage increased with increased RCA replacement percentages and water-to-cement ratios; however, it decreased when fly ash and superplasticizers were applied [26,27].

In recent years, RCA has been demonstrated to be a promising technique for adding sustainability characteristics to traditional concrete mixtures [28]. Several benefits can result from the use of RA rather than natural aggregates, including a reduction of production costs and the ability to ensure a high level of availability. In comparison with conventional concrete, the cost of replacing RA in 100, 50, and 30% of a fly ash cement composite was compared by Wang et al. [29]. Despite having 2% less strength than its target strength (27.2 MPa), the 30 and 50% fly ash RCA was 15 and 26.5%, respectively, less expensive than conventional concrete. Although these savings may not seem significant, RA could be used to replace NA concrete by up to 100% [30]. Furthermore, the costs for the manufacture of cement composites are further reduced by accounting for the disposal income from construction waste

Nevertheless, it is important to recognize that a major challenge lies in the perception of trustworthiness among users of these materials [31]. The environmental benefits of recycling concrete often outweigh the economic benefits of landfilling or disposing of it. Using this method will reduce pollution, transportation costs, and production costs of concrete, thereby reducing the consumption of natural resources. Since RCA originates from a wide variety of sources, its high degree of variability makes incorporating it into freshly cast concrete an extremely difficult process. The lack of specific guidelines regarding RCA specifications and their physical, chemical, and mechanical properties is another factor that needs to be addressed [32]. In concrete mixes containing RA, the negative chemical properties of the RA can lead to deterioration during use, which can negatively affect the durability and performance of the concrete mix. As well, it is critical to pay attention to other concerns related to physical conditions, (e.g., size, type, angularity, and texture of RA) [33].

CDW can be recycled or reprocessed to replace a substantial proportion of construction materials in many developing countries. The problem is insufficient regulations and a lack of awareness of the advantages of these options. Developed countries are making efforts to promote the use of CDW globally. Therefore, it is likely that in the near future, RA derived from CDW will play a significant role in the commercial industry. The availability of landfill land is decreasing, and the aggregate demand for solid waste is approaching 40 billion tons per year. Due to this particular need, CDW can be viewed as a viable alternative to landfills. Nevertheless, research and development efforts will be required in order to find alternative materials that can be used for the production of concrete containing RA [34].

Random Forest (RF) algorithm is a collective learning method that involves inputting data into an ensemble and developing decision trees during the training process to determine a regression model [35,36]. Breiman [37] developed the method by combining bagging sampling [38] and random selection of features [39,40]. A decision tree based on controlled variation has been developed by combining these two methods. The RFs approach utilizes trees as the basis for determining the classification label for every unlabeled instance in the ensemble. In the past decade, RF has become increasingly relevant across almost all disciplines, leading to numerous applications in almost every field, and many more are still in development.

The RFs method, for example, has been effectively utilized to model the properties of subsoils under a variety of conditions [41-44]. The effectiveness of this method has been demonstrated to be reasonable in predicting the behavior of various types of deep foundations [45-47]. A variety of construction management and engineering studies have also successfully applied the method in recent years [48-50]. This approach has also been successful in forecasting pavement material characteristics [51-53]. The modeling approach has been extensively used to model the characteristics of cement-based materials during their fresh and hardened states for the past few decades [54-63].

Despite its cost and carbon footprint advantages, RACs have not been used more in construction because of their inferior mechanical and durability properties. By including the appropriate SCMs, the harmful impacts of RCA may be mitigated in concrete. Owing to the vast chemical variety of SCMs and their combinations, material development research may need extensive testing, leading to costly experimental campaigns. This work provides a dependable RF model for predicting and evaluating the CS of concretes incorporating RCAs, even when SCMs are present. This approach is efficient for decreasing development costs and timelines for novel doses.

Breiman et al. [74] introduced classification and regression trees (CART) in 1984, an innovative data analysis technique based on computational modeling. CART, sometimes known as a decision tree, has been used for classification and regression issues. A CART model conceptually resembles an inverted tree. This paradigm has both terminal and non-terminal nodes [75]. The solution to a query with two alternative answers should be a non-terminal node that indicates the direction in which two derivative nodes will progress.

The terminal nodes, on the other hand, offer a final forecast [75]. After the strategy has been modified, predicting a reaction is straightforward. With a given set of input variable values, following the tree's path from the root to the terminal nodes is sufficient, answering the questions presented at the non-terminal nodes up to the predicted response value of the response [75]. If the criteria at the non-terminal node is met, the CART model must go to the node on the left; otherwise, it must proceed to the node on the right. According to Genuer and Poggi [75], a CART model entails dividing a space into rational and binary sections, then selecting the best out of both of these divisions that will produce the desired response. Thus, two phases are required to create this prediction technique. Initial construction of a comprehensive CART model must include all terminal and non-terminal nodes and their respective link routes. Then, it is required to prune the whole CART strategy in order to generate optimum subtrees which is picked as the best suitable tree that ensures there is no model overfitting concerns. See references [74-75] for further information on the CART algorithm's technique.

A Random Forest technique is a machine learning paradigm that integrates numerous tree-prediction models, according to Dietterich [76]. In a regression problem, the ensemble technique estimates the response based on the midpoint of the forecasts from all tree models. The ensemble approach, on the other hand, utilizes a simple majority to solve a classification problem. Since the study given in this publication relies on regression methods, the following explanation focuses on this kind of analysis. The Random Forest regression model consists of m tree-based models . Each CART model is trained using a distinct subset of the total train data [37]. In order to adapt the tree-based techniques, a bootstrapping algorithm picks many random subgroups of data of the same size. As a result, the remaining dataset is not used for this model since each CART model is trained using just a subset of the complete data. Hence, the out-of-bag sample (OOB) data subset might be defined as the fraction of data not used to train a CART [55].

Furthermore, it is vital to specify the two characteristics that must be satisfied for the ensemble technique to be more successful than CART methods used individually. The first criterion is that the performance of any tree model must surpass that of random predictors. The second criterion is that each of the techniques included in the ensembled model must be distinct, i.e., there must be no connection between their mistakes [77]. As seen in Eq. (7), the forecasting approach employed by the Random Forest regression can be computed as the average value of the forecastings of all trees that compound the ensembled model.

Where is the forecast of the response performed by the i regression tree approach, being θ _i the bootstrap sampling utilized to fit the individual model.

According to Oshiro et al. [78], increasing the number of trees does not guarantee that the Random Forest method would outperform the previous one (where the number of trees was lower), and increasing the number of trees by a factor of two is illogical. Hence, the Random Forest method takes into consideration an optimal number of CART models [63,78]. References [37,63] can be consulted for a deeper knowledge of these machine-learning methodologies.

Using fourteen input variables, the current study proposes a Random Forest regression model designed to predict the compressive strength of RAC, even when utilizing SCMs. Table 1 contains the definitions of the considered input variables.

Using a cross-validation process, the Random Forest regression models were evaluated on the testing subset and modified using the test data. This sort of training aids in avoiding the overfitting and bias difficulties that these machine learning strategies often encounter [79]. In addition, to confirm the validity of the findings, this extra validation process and six statistical performance measures were applied to each of the generated models. Viz., the root of the mean squared error (RMSE), the mean absolute error (MAE), the normalized mean bias error (NMBE), the ratio of the RMSE to the standard deviation of measured data (RSR), the Nash coefficient of efficiency (E), and the coefficient of determination (R²), whose formulations are presented in Eqs. (8-13) respectively. The use of multi-fitness criteria to ensure the correctness of the suggested techniques is made possible by the combination of different statistical indices that may overcome some of the limits of each individual one [79].

being a database's real value of the dependant variable; Whereas ā represents the mean of the answers to the data, â is the result of the Random Forest regression method, and n is the total number of observations.

With the Random Forest method, one approach to determine the importance of a variable is to observe how much the model's goodness-of-fit reduces if the variable is removed [37]. Since that each tree-based model has its own OOB data subset, this may be used to determine the significance of a certain input component. Specifically, the OOB predicting performance is calculated for each particular CART technique. The OOB input variable is then randomly shuffled while maintaining the significance of the other components. The forecast accuracy decline resulting from the rearranged data is then calculated. Thus, the estimation of the factor significance of the j input component in the i CART method may be estimated as shown in Eq. (14):

being mse the mean squared error of the forecasting, and represents the forecasting estimated by the individual tree-based regression on the OOB _i data subset, removing the factor j.

In the end, the j input's variable importance metrics may be calculated for the Random Forest regression by determining the average variable relevance of each tree model, as shown in Eq. (15):

where I _j,RF represents the importance of the input variable j on the considered response as per the ensembled Random Forest regression approach, I _j,i represents the importante of that input variable according to the individual tree-based model i, and m is the total number of trees in the Random Forest model.

In this research, the Random Forest regression models were made with the help of the R statistical and programming language [80] and the randomForest package [75]. When the models were being trained, a limit of 1,000 CARTs per model was considered. The number of trees that led to the minor RMSE was used was chosen on the test data subset, as presented in Fig. 1. According to that analysis, a number of 563 CART models was selected for the RF approach.

Figure 1 Source: The authors

Fig. 2 shows the first CART individual regression model for the Random Forest method to predict the concrete compressive strength.

Figure 2 Source: The authors

The results of the performance metrics measured in both data subsets is presented in Table 2. Moreover, the regression plot is put forward in Fig. 3. From the analysis of these results, it can be concluded the good efficiency of the model in prediction the CS of RAC even with SCMs.

Table 2

Subset	RMSE	MAE	NMBE	RSR	E	R2
Train	3.548	2.047	0.424%	0.292	0.915	0.919
Test	3.846	2.869	-0.397%	0.317	0.899	0.901

Source: The authors.

Figure 3 Source: The authors

As can be appreciated in Fig. 3 and Table 2, results on train and test data subsets are similar, which points out the good performance of the model regarding overfitting [59,72].

Fig. 4 present the results of the Variable Importance (VI) in RF approach. The correlation between the input factors and the compressive strength of the RAC was examined in this instance in order to gain insight into their relationship. The study found that, in that order, silica fume (I2), RM (I4), and cement dosage (I1) had the most significant influence on the result. Silica fume is known to have significant pozzolanic reactivity due to its tiny particle size (about 150 nm) and high amorphous SiO₂ concentration. It forms a CSH gel when it reacts with the pore solution's Ca(OH)₂. The increase in CSH leads to the refining of the pore structure of

Figure 4 Source: The authors

the cementitious paste. This modification contributes to the enhancement of concrete's mechanical characteristics, particularly its CS [81]. RM is the second most influential parameter on the CS of concrete. Its reactivity is connected to the cement dosage, the most important contributor to this modulus. Moreover, certain SCMs with a high CaO concentration, such as blast furnace slag and type C fly ash, may create cementitious products, enhancing the mechanical properties of the cement paste and the concrete [82]. Researchers determined that adding cement or SCMs with high hydraulic reactivity [83] is a good strategy to mitigate the resistance losses caused by using recycled aggregates, hence validating the VI findings.

Regarding the cement content (I1), it is well known that cement is the principal source of hydration products that are responsible for the increased density and strength, even when RCAs are used [84].

As per [85], some other RAC features have a significant beneficial effect on the reaction of concrete to compressive stresses. These variables include silica modulus (I5), coarse NA content (I9), fine NA content (I8), SCMs excluding silica fume (I3), and superplasticizer dose (I12). Supplementary cementitious materials with high silicon and aluminum content, such as type F fly ash, recycled glass powder, rice husk ash, and metakaolin, possess pozzolanic properties. It has been demonstrated that in adequate proportions, they contribute to the increase in strength, particularly at advanced ages (e.g., after 56 days of curing), as they can react with the water and calcium hydroxide to produce calcium silicate hydrates (CSH) or calcium (CASH). Hydration products contribute to the cement matrix's densification and concrete's mechanical performance at advanced ages [17]. Certain SCMs have hydraulic characteristics that enable them to react with water to form cement-like hydration products [86]. The VI analysis demonstrates that these SCMs contribute to the RM index (I4). The research revealed, however, that the content of SCMs (I3) seems to be of minimal significance, indicating that it is not the dosage of SCMs that is significant but rather their nature. Hence, if these SCMs have hydraulic (recognized by the RM index) or pozzolanic (identified by the SM index) capabilities on the siliceous side, the impact will be favorable. Nevertheless, it will be exposed later that the impact will be notably negative if the pozzolanic characteristics are on the aluminum side (as determined by the AM modulus).

Research [87,88] have indicated that the proportion of NAs replaced with RCAs reduces the compressive strength of concretes with comparable w/b ratios. This is mostly due to the higher water demand required to produce concrete workability and adequate hydration of cement paste and/or cementitious components. RCAs often have greater porosity than NAs and may retain residues of mortar and carbonated hydration products, resulting in lower effective bonding of cementitious elements in the new concrete and, as a result, fewer nucleation sites for freshly created CSH or CASH. The study's findings suggest that superplasticizers are essential for controlling the increasing demand for water in recycled aggregate concrete mixes. Hence, using superplasticizers favors the compressive strength (CS) of concrete, including RCAs, by decreasing the needed water content for such mixes, enhancing CS. When paired with the use of SCMs, its beneficial impact is supposed to compensate for the drop in CS caused by the use of RCAs [89-91]. However, the significance of the SCM appears to be limited in Fig. 4. Nevertheless, the impact of the superplasticizer (I12) on CS seems to be restricted and perhaps obscured by the impacts and interactions of the cement content (I1) and water (I11). It is important to note that superplasticizers are supposed to substantially affect the cement-water system [92]. The water content (I11), the w/b ratio (I14), and the coarse RA are among the most important input factors that negatively impact the CS of concrete containing RCAs [85]. Hence its importance, as observed in Fig. 4, where it can be seen that these factors occupy the fifth and sixth place in relevance. The negative impact of these factors on the compression response of RAC is consistent with the current literature, which demonstrates that water and the w/b ratio have a well-known detrimental effect on the mechanical resistance of concrete. In addition, several studies have shown that using RCAs reduces the CS of concrete proportionally to the replacement volume due to the great porosity, low resistance, and high-water absorption of these recycled aggregates. Hence, it is possible to deduce that recycled aggregates enhance the porosity of concrete, leading to a lower density and CS [88, 93-95].

Fine RA (I8), AM modulus of cementitious materials (I6), and MSA (I13) have a reduced effect on the CS of RAC concrete. Recent research has proved that these factors are harmful but not especially relevant for CS [85]. The impact of SCMs with a high aluminum content on RAC performance is particularly intriguing. Despite their high pozzolanic reactivity index, these components have a detrimental effect on the compressive strength of RAC concretes, according to the VI findings. Many mechanisms may explain this phenomenon, including the production of CASH-type gel compounds and the decrease in pH of the pore solution owing to the high aluminosilicate concentration. Even though this reaction initially enhances mechanical qualities, it is detrimental in the long run [96]. In addition, several research [96,97] observed that the chemical interaction of reactive SiO₂ and Al₂O₃ concentration in SCMs with a high AM modulus increases the temperature during the cement's hydration process, resulting in decreased flowability, which could negatively affect the pouring process and the final mechanical performance of the concrete. In addition, several investigations have shown that more water or superplasticizer is necessary to obtain the appropriate workability when employing SCMs with a high alumina modulus [98-102]. Considering the unique situation of RCAs regarding porosity and water demand, the higher water needs of SCMs with high AM values may explain the findings reported in Fig. 4.

The CS of concrete made only with NAs is influenced by the maximum size of the aggregate (I13). Studies have shown that smaller aggregate sizes require larger amounts of cement paste to achieve a given resistance [59, 103]. Therefore, it can be concluded that a larger MSA should positively influence the CS of concrete. However, in the case of RAC, MSA (I13) has a noticeably negative impact on CS. The reason for this change in trend can be attributed to the fact that the thickness of the interstitial transition zone is directly proportional to the aggregate size [103], and in concrete with recycled aggregate, this zone is even more porous than in concrete made with only NAs, which impairs the CS of the concrete [104]. Hence, as the mixtures in the database combined NA and RCA, this factor appears to have a little significance as per Fig. 4.