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-Effective water/cement ratio of all concrete mixes 

-Effective water/cement ratio of all concrete mixes 

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This paper intends to analyze the microstructure of concrete with recycled aggregates (RA) from construction and demolition waste from various Portuguese recycling plants. To that effect, several scanning electron microscopy (SEM) and energy-dispersive X-ray spectroscopy (EDS) analyses were performed. Various concrete mixes were evaluated in order...

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... mix produced had a 125 ± 15 mm slump, in order to compare mixes with the same application range, A preliminary stage was needed to adjust, whenever necessary, the water content of each concrete mix in order to fulfil this requirement. Table 1 shows that the effective w/c ratio had to be raised as the RA content increased. This increase was not the same in all the families of RA mixes. ...

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... Mix M-CB, made with crushed clay bricks, had a compressive strength of 68.7 MPa and was well-hydrated with good mechanical properties, as indicated by the presence of C-S-H and ITZ as shown inFig. 9[36,37]. ...
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... The study concluded that use of coarse RA reduces the durability of concrete and water absorption tends to increase linearly with increase in percentage of coarse aggregate replacement. Bravo et al. [7] performed an analysis on the microstructure of concrete with recycled aggregates from construction and demolition waste from different sources in Portugal. Study concluded that the bonding capacity of the aggregate to cement paste is greatly influenced by the nature of RA. ...
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... Construction and demolition waste (CDW) has been extensively used in the construction industry since the second world war considering the massive amount of debris and the desire to meet the increasing demand for suitable construction materials [138,139]. In EU countries, roughly 50% of the total volume of CDW is recycled, and about 70% of the total CDW amount is expected to be reused by 2020 [140]. In the US, nearly 136.1 Mt of waste was produced by construction and demolition activities, but merely 28% were recycled [141]. ...
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... Regarding the drd and the dssd, three homogeneous groups without statistically significant differences can be observed (Figure 4a,b): the group of natural aggregates (CNA, Ru), Rb and masonry mortar (Rc2), and concrete particles (Rc1). It has been proven that cementitious particles (Rc1 and Rc2) present lower values than natural aggregates in drd and dssd [21][22][23][24][25][26][27]. However, natural aggregates, Rb, and Rc1 had similar dap, while Rc2 had the lowest value ( Figure 4c) and presented significant differences. ...
... Apparent particle density (d ap ) 9.32 1 × 10 −4 Oven-dried particle density (d rd ) 62.05 1 × 10 −4 Saturated and surface dried particle density (d ssd ) 43 Regarding the d rd and the d ssd , three homogeneous groups without statistically significant differences can be observed (Figure 4a,b): the group of natural aggregates (CNA, Ru), Rb and masonry mortar (Rc2), and concrete particles (Rc1). It has been proven that cementitious particles (Rc1 and Rc2) present lower values than natural aggregates in d rd and d ssd [21][22][23][24][25][26][27]. However, natural aggregates, Rb, and Rc1 had similar d ap , while Rc2 had the lowest value ( Figure 4c) and presented significant differences. ...
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... [26] When the RAC is stressed, the cracks start from the fragile area near the ITZ and gradually spread to the aggregate and cementitious materials, resulting in the destruction of the entire concrete [24,28]. It has been found that ITZ is composed of pores, Ca(OH) 2 , C-S-H gel, ettringite and cement particles [29]. At the same time, it can be found that the volume ratio of C-S-H in the ITZ between the aggregate and the new cementitious material is greater than that of the old cementitious material, as shown in Figure 2 [29]. ...
... It has been found that ITZ is composed of pores, Ca(OH) 2 , C-S-H gel, ettringite and cement particles [29]. At the same time, it can be found that the volume ratio of C-S-H in the ITZ between the aggregate and the new cementitious material is greater than that of the old cementitious material, as shown in Figure 2 [29]. Studies have shown that the characteristics of ITZ in RAC are related to the quality of the attached mortar and have nothing to do with the quantity of mortar [30]. ...
... Because RCA is attached to more residual gelling materials, the thickness of ITZ in NAC is usually 9-51 µm, and the thickness of ITZ in RAC is 30-60 µm [31,32]. [29] On this basis, some scholars continue to deepen the study of the microstructure of RAC and found that the strength of ITZ is more affected by the water-to-binder ratio. In the lower water-binder ratio concrete, its strength is mainly affected by the ITZ between the residual cementitious materials, and the new ITZ mainly affects the high water-binder ratio concrete components. ...
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... As for CRA, the highest decrease was obtained when 100% of aggregates from Valnor were used (22.1%), and the difference between families of CRA was much lower than that for FRA. Besides some factors mentioned above (such as a high amount of clay materials, strength of RA and higher w/c ratio needed to maintain workability), the microscopic and durability test performed on FRA from Vimajas [8,42] allowed us to conclude that these were highly porous, thus also leading to a highly porous concrete. Kim and Yun [43] evaluated the bond-slip between steel and concrete with CRA and pointed out that the quality of concrete near the rebars, especially its porosity, highly influences the bond strength obtained. ...
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This works intends to analyze, experimentally and numerically, the bond-slip behavior between steel and concrete made with recycled aggregates (RA) from construction and demolition waste (CDW) from several recycling plants in Portugal. Pull-out tests performed in concrete mixes with RA from CDW are described and the main results (bond strength, bond-slip curves and failure modes) are shown and discussed. Additionally, a comparison between experimental and analytical (using equations from the literature) results is made. Afterwards, finite element (FE) models using Abaqus are developed and compared with the experimental results. The interface behavior between steel and concrete follows that prescribed by the CEB-FIP Model Code and uses as input experimental results. After validation, the models show good results when extended to predict the bond-slip behavior of the remaining concrete mixes studied. It is generally concluded that, per each 10% of natural aggregates replaced with RA from CDW, the bond strength decreases in circa 3% (numerically) to 5% (experimentally). CEB-FIP Model Code equations are shown to be able to predict bond strength and, when used in FE models, to lead to accurate simulation of the bond-slip response of steel and concrete with RA from CDW: the average ratio between numerical and experimental bond strengths is 0.95. In the scope of the FE models developed, a simple equation to be used along with those prescribed by CEB-FIP, which accounts for fraction and ratio of aggregates replaced, is put forward, as a first approach, showing good results.
... Yet the SEM has a relatively higher cost (28). Despite its, most of the studies on RAC microstructure investigations used images from SEM to characterize the morphological features of the ITZ, or even other much more expensive techniques (24,29,30). Considering that the resolution of the imaging determines the range of pore sizes accessible, OM may be appropriate for studying the pore formation and the distribution of their components on RC microstructure, given that it is widely used in petrographic and metallographic studies; therefore, it can also be valid for use in both laboratory and industrial-scale applications (31)(32)(33). ...
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Recycled concrete has a microstructure more complex than natural concrete, as it includes new interfacial transition zones, the quality of which is conditioned by the state of humidity of the aggregates used, which in turn will affect the final properties of the concrete. Bearing in mind the greater absorption capacity of recycled aggregates, it is important to improve its properties by means of a treatment method that is capable of reducing the negative effects that this may produce in the new concrete. Therefore, the influence of the pre-soaking method of recycled aggregates on the formation of the microstructure of concretes manufactured with these aggregates is analysed, to determine which treatment is the most effective for the production of concretes for non-structural use. The results show that the microstructure of the evaluated concretes differs according to the treatment method used, the most optimal method being one that uses aggregates without pre-soaking.