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Article

The Effect of Waste Ballast Aggregates on Mechanical and Durability Properties of Standard Concrete

by
Hasan Erhan Yücel
1,
Maciej Dutkiewicz
2,* and
Fatih Yıldızhan
3
1
Civil Engineering Department, Engineering Faculty, Niğde Ömer Halisdemir University, Niğde 51240, Turkey
2
Faculty of Civil and Environmental Engineering and Architecture, Bydgoszcz University of Science and Technology, 85-796 Bydgoszcz, Poland
3
Civil Engineering Department, Engineering Faculty, Gaziantep University, Gaziantep 27310, Turkey
*
Author to whom correspondence should be addressed.
Materials 2023, 16(7), 2665; https://doi.org/10.3390/ma16072665
Submission received: 30 December 2022 / Revised: 23 March 2023 / Accepted: 24 March 2023 / Published: 27 March 2023
(This article belongs to the Special Issue Recycled Aggregate in Concrete Applications)

Abstract

:
The acquisition and transportation of aggregate exacerbate the negative impact of concrete on the environment, and waste materials are considered an effective solution to this crucial problem. One of these waste materials is waste ballast (WB), which is needed for new infrastructure along with increasing rail track technology. In this study, the effect of WB aggregate (which is basalt-based) on the mechanical and durability properties of standard concrete was examined. Coarse aggregate was replaced with WB aggregate at the rates of 50%, 75% and 100%. The slump, compressive strength, flexural strength, capillary water absorption, rapid chloride permeability and water penetration tests on the mixtures were performed. According to the results of this study, the utilization of WB improved the compressive strength and flexural strength of the mixtures by about 15% and 7%, respectively. Moreover, the capillary water absorption, rapid chloride permeability and water penetration values of all the concrete mixtures with WB were lower than the control mixture. In addition, the correlation relations between the mechanical and durability properties indicated that they have a strong relationship with each other. All the results of this study demonstrated that the utilization of WB instead of coarse aggregate improved the mechanical and durability properties of concrete. WB can also provide a more sustainable material formation by minimizing the negative environmental effects of concrete production.

1. Introduction

Industrialization and related rapid urbanization have provided health, economic and technological development and also have led to many changes in human life [1,2]. One of these changes has been in the construction industry [3]. In the 19th and 20th centuries, the construction sector became one of the largest industries, with rapid developments such as concrete, steel-reinforced concrete, prestressed concrete, high-strength concrete and fibre-reinforced concrete [1,4]. This rapid development has made concrete the second most-used material after water [1]. Although the widespread use of concrete has provided advantages such as low cost, high compressive strength and durability, on-site or precast production, etc. [5], it has caused many negativities [6]. It is possible to deal with these negatives under two main headings: the excessive construction/demolition waste generated from aged structures and the environmental negative effects of concrete production.
Construction/demolition waste is increasing day by day because of the increase in the world’s population and the development of construction technology. For example, a total of 2533 million tons of waste was generated in the European Union, and about 922 tons of this waste belonged to construction/demolition waste in 2016 [7]. The amount of waste was 2.01 billion tons worldwide in 2016, and it is expected that the waste will increase to 3.40 billion tons by 2050 [8,9]. Furthermore, the landfill requirement for municipal solid waste disposal in India is expected to reach 169.6 km2 by 2047. This area is approximately eight times higher than in 1997 [2,10,11]. These wastes cause serious health, economic and environmental problems [8,12,13]. The recycling rate of construction/demolition waste in EU countries varies and the average recycling rate of construction/demolition waste in 27 EU countries is 55% [14,15]. This situation shows that the recycling rate of construction/demolition waste should be increased.
Another crucial problem is the negative environmental effects of concrete production. Cement production is responsible for 8% of the total CO2 emissions [1] and 36% of the CO2 emitted globally by construction activities [6,16]. The acquisition and transportation of aggregate further increases the negative effect of concrete [17] and concrete is responsible for 10% of the total CO2 emissions [18,19,20]. With the increasing demand, the need for these materials is constantly increasing. The annual concrete consumption is more than 10 billion tons [21,22,23], and it is expected to increase to about 18 million by 2050 [22,24]. The annual cement requirement for the concrete industry is 1.5 billion tons, the aggregate is 10–20 billion tons and the water requirement is approximately 1 million tons [21,25,26]. In addition, the global aggregate use in the construction industry reached 48 billion tons [27,28]. Most aggregates are obtained from natural deposits. For example, the rate of aggregate obtained from natural deposits is 91% in Europe [29]. The acquisition of natural aggregate causes erosion of the river deltas and coastlines [21,30]. Moreover, a shortage of aggregate is another problem to be considered [31]. Therefore, the International Energy Agency recommends the use of different materials instead of natural aggregates [21,32]. Considering all these problems, it can be said that the best way is to recycle waste and use it instead of aggregate [33].
The idea of more reliable solutions and materials that meet the principle of sustainable development is important for the development of new concretes and mortars [34,35].
The use of waste materials instead of aggregate has been tried in many studies [36,37,38,39]. Moreover, many countries have started the application of utilizing recycled aggregate in this sense. For example, the first attempts to recycle construction/demolition waste started in Germany in the 1980s. Later, many countries made progress toward this aim [36]. One of the construction/demolition wastes used in these applications is waste ballast (WB). A large amount of WB is formed due to the increasing need for new infrastructure along with developing rail track technology [40]. For example, Indian railways supplied around eight million cubic meters of ballast in 2017–2018 [41,42]. Ballast materials are high quality igneous or metamorphic rocks. In addition, their particle size, particle shape, strength, hardness and resistance properties are of a quality that satisfies certain criteria [43]. Generally, basalt and granite are used as ballast materials [44]. Korkanç and Tuğrul [45] also stated that the mechanical properties of basalts are appropriate for use as aggregates for concrete production. Therefore, positive results were obtained in the applications of recycling WB. WB was tested for self-compacting recycled aggregate concrete [7], recycled aggregate mortar [46], over-burnt brick ballast aggregate concrete [3] and preplaced aggregate concrete [47]. Furthermore, it was tested for the partial replacement of coarse aggregate in concrete to some extent (up to 20%) [17].
As of 2020, there was a total of 12,803 km of national railway network in Turkey, of which there were 11,590 km of conventional lines and 1213 km of high-speed lines [48]. Considering Turkey in general, it is thought that approximately 5440 tons of waste ballast is produced annually. For this reason, the recycling of waste ballast, which is produced in large quantities in Turkey, is very important. In addition, since it is known that high quality aggregates such as basalt are generally used as a ballast aggregate in Turkey, it was thought that the ballast aggregate obtained as waste could be used in concrete production.
The capability of using the higher amount of WB and its evaluation based on its strength and durability properties in conventional concrete is a promising issue. The high available amount, the superior quality, the targeting of high rates in recycling and the positive results obtained from WB in the literature support this idea. In the literature, there are very limited studies that have observed WB aggregates used in concrete, and in these studies, the ratio of replacement with normal aggregates is at a maximum 40%. In addition, these studies only focused on the strength, freezing–thawing and shrinkage properties. Within the scope of this study, the effect of WB aggregate (which is basalt-based) on the mechanical and permeability properties, which are very important for the durability properties of concrete, was investigated. Coarse aggregate was replaced with WB aggregate at the rates of 50%, 75% and 100%. In addition, C30/37 concrete was produced as the control mixture. The slump, compressive strength, flexural strength, capillary water absorption, rapid chloride permeability and water penetration tests on the mixtures were performed and the effect of WB was evaluated. Finally, correlation relations between mechanical and durability properties were determined.

2. Experimental Program

2.1. Materials

Standard CEM I 42.5 R Portland cement was used in all mixtures. The chemical composition and physical properties of Portland cement are presented in Table 1. Figure 1 shows the particle size distribution of aggregate and cement. Figure 2 presents natural sand, crushed stone and WB. Natural sand aggregate between 0–4 mm was used as a fine aggregate. The specific gravity of natural sand is 2.67, its water absorption rate is 2.65% and its natural humidity is 0.8%. Crushed stone aggregate between 4–16 mm was used as coarse aggregate. The specific gravity of crushed stone is 2.65, its water absorption rate is 0.9% and its natural humidity is 0.81%. Finally, the specific gravity of the WB aggregate is 2.67 and its water absorption rate is 0.7%. As can be seen in Figure 2, WB has an irregular and elongated shape.
In order for an aggregate to be used as a ballast, the mass losses obtained in the Los Angeles fragmentation resistance determination, frost resistance determination and abrasion resistance determination tests must be equal to or lower than 14%, 3% and 12%, respectively [49]. The above-mentioned tests were applied to the aggregates used as ballasts at certain periods, and the aggregates below these values were stored as waste ballasts. The waste ballast aggregate stored in the Kayseri region in Turkey was used as the WB in this study. The WB was obtained as a result of the wear of the basalt aggregate produced in the Kayseri region as a result of using it as a ballast.

2.2. Mix Design of Concrete

Four mixtures were prepared with the proportions shown in Table 2. When the studies in the literature were examined, it was seen that the ballast aggregate was replaced with normal aggregate at the maximum rate of 40% in the concrete mixtures [3,50]. This rate was 25%, 50%, 75% and 100% in the studies where other recycled aggregates were used, especially for basalt-based recycled aggregates [7,18,29,46,51,52,53]. Because of this, the aggregate used in this study was high-quality waste basalt-based ballast aggregate, and the coarse aggregate was replaced with WB at a rate of 50%, 75% and 100%, respectively. WB50 refers to 50%, WB75 refers to 75%, and WB100 refers to 100% utilization of WB. For the aggregate, the most ideal mixture was found with the use of 60% crushed stone aggregate and 40% natural sand. After determining the aggregate ratio to be used, the targeted concrete compressive strength of the concrete to be produced was determined as C30/37. Firstly, the slump tests on the mixtures were performed according to ASTM C143. The slump value was used to check whether the design was performed correctly or not, because it is a significant parameter in the design of a concrete mixture. The experiment was performed as follows: fresh concrete was placed in the mold in three layers, with each layer filling approximately one-third of the mold. Each placed layer was tamped 25 times with a tamping rod. Mold was slowly pulled vertically upwards and the slump values of the mixtures were measured.

2.3. Test Procedures

2.3.1. Compressive and Flexural Strength Test

The compressive and flexural strengths of the mixtures were determined with respect to ASTM C 39 [54] and ASTM C 78 [55] at 7 and 28 days, respectively. The compressive and flexural test setups are displayed in Figure 3a,b, respectively. Six cubic specimens with the dimension of 150 mm × 150 mm × 150 mm were tested to determine the compressive strength of each mixture. For the flexural test, six prism specimens with the dimension of 100 mm × 100 mm × 500 mm were used. The compressive and flexural strengths were determined considering the average values of these specimens.

2.3.2. Capillary Water Absorption

The capillary water absorption of the mixtures was determined with respect to ASTM C1585 [56] at 7 and 28 days. The capillary water absorption test procedure is shown in Figure 3c. Three samples of each mixture were kept in a 100 °C oven for 24 h and completely dried. Then, the samples were coated with epoxy to prevent water absorption from their surfaces, except for the surface touching the water. Finally, the sides of the samples that were not coated with epoxy were placed on the tray in contact with water and their weights were measured at regular periods.

2.3.3. Rapid Chloride Permeability

The rapid chloride permeability tests of the specimens were carried out according to ASTM C1202 [57] at 7 and 28 days. The rapid chloride permeability test setup is shown in Figure 3d. The tests were performed on three specimens with a height of 50 mm and a diameter of 100 mm. The specimens were placed between two cells, one with a 3.0% salt (NaCl) solution and the other with a 0.3 M sodium hydroxide (NaOH) solution. Finally, the electrodes were immersed in the cells with a voltage of 60 V and the rapid chloride permeability was calculated according to the charge that passed through the specimens.

2.3.4. Water Penetration Test

The depth of water penetration was determined with respect to BS EN 12390-8 [58]. The water penetration test procedure is displayed in Figure 3e. This experiment was carried out on standard cured samples at 7 days and 28 days, respectively. The samples removed from curing were allowed to dry for approximately 5 h in the laboratory environment. Silicone material was used for the side surface of the samples. The samples, which were coated with silicone material, were left to dry. In the experiment, water was applied to the bottom surface of the samples under 5 bar pressure for 72 h. Afterwards, the samples were removed from the device and the depth of the water penetration in the hardened concrete specimens under pressure was determined by splitting the sample in half, perpendicular to the surface to which the pressurized water was applied.

3. Results and Discussion

3.1. Compressive Strength Test

The compressive strength test results of the mixtures are shown in Figure 4. As the amount of WB increased, the compressive strength of the mixtures increased. The compressive strength increased by 6.57%, 10.41% and 15.44% for WB50, WB75 and WB100, compared to the control mixture at 7 days, respectively. Moreover, at 28 days, the compressive strength increased in the range of 7.23%, 9.45% and 15.08%, respectively. According to these results, the WB positively affected the compressive strength. This improvement can be attributed to the good quality of the WB [7,59] and also to the irregular particle shape of the WB, which causes an increment in the adhesion between the paste and WB [51]. There are some studies in the literature about the utilization of WB or basalt that increases the compressive strength. Dasari et al. [17] used 5%, 10%, 15% and 20% WB instead of coarse aggregate. The compressive strength increased as the amount of WB increased. Aja et al. [7] indicated that concrete with recycled ballast could fulfil the requirement for the compressive strength of a slab track. Özturan and Çeçen [60] stated that concrete with basalt aggregate provides a higher strength than concrete using limestone and gravel aggregate. Kishore et al. [61] tested the basalt replacement of coarse aggregate at a rate of 0% to 100% by steps of 25% increments and found that the utilization of basalt increased the compressive strength. Boğa and Şenol [52] used basalt instead of crushed stone for high-strength self-compacting concrete. The basalt replacement of crushed stone at rates of 25%, 50%, 75% and 100% were tested, and the 100% utilization of basalt had the highest compressive strength, and this was also higher than the control mixture. Ajdukiewicz and Kliszczewicz [62] also supported these results and reported that the concrete with waste basalt and natural basalt had similar mechanical properties. These findings showed that waste basalt, which is a type of ballast material and natural basalt, gave similar results and also improved the compressive strength. According to the test results, the WB used in the study increased the compressive strength, although it was less than that reported by studies in the literature. This can be explained by the use of WB at a much higher replacement ratio compared to the literature.

3.2. Flexural Strength Test

The flexural strength test results of the mixtures are given in Figure 5. The minimum and maximum flexural strengths were obtained from the control mixture and WB100 at 7 and 28 days, respectively. The flexural strength of WB100 at 7 and 28 days, increased in the ratios of 6.40% and 7.20% compared to the control mixture, respectively. WB enhanced the flexural strength of the mixtures. This improvement can be explained by the irregular and elongated shape of WB [51]. Similarly, Dasari et al. [17] studied a 20% WB replacement of coarse aggregate and an increment of 17.49% and 19.11% was observed in the 7- and 28-day flexural strengths, respectively. Ali et al. [3] tried over-burnt brick ballast instead of coarse aggregate and the utilization of 20% WB increased the 28-day flexural strength by 30% compared to the control mixture. Özturan and Çeçen [60] expressed that concrete with basalt aggregate provides a higher strength than concrete using gravel aggregate. According to the test results, the WB used in the study increased the flexural strength, although it was less than that reported by studies in the literature. This can be explained by the use of WB at a much higher replacement ratio compared to the literature.

3.3. Capillary Water Absorption

The capillary water absorption values of the mixtures are graphically presented in Figure 6. As can be seen in Figure 6, the capillary water absorption value decreased when the amount of WB increased. The 7-day and 28-day capillary water absorption values of the control mixture were 0.278 mm/min0.5 and 0.039 mm/min0.5, respectively, whereas the 7-day and 28-day capillary water absorption values of the WB100 were 0.253 mm/min0.5 and 0.032 mm/min0.5, respectively. Therefore, it was determined that there was a 9% and 18% reduction in the capillary water absorption values for 7 and 28 days, respectively. This finding shows that WB reduced the capillary water absorption and composed a more impermeable concrete than the control mixture. This situation can be explained by the low void and water absorption values of WB [63,64]. When the test results were examined, it was determined that the WB used in this study had a more positive effect on the capillary water absorption than the studies in the literature.

3.4. Rapid Chloride Permeability

The rapid chloride permeability test results of the mixtures are plotted in Figure 7. The 7-day and 28-day rapid chloride permeability values were in the range of 6161–9613 and 4842–6384 coulombs, respectively. The rapid chloride permeability value of WB100 was 35.91% less at 7 days and 24.10% at 28 days, compared to the control mixture. The rapid chloride permeability decreased as the WB increased. This finding indicates that the WB improved the impermeability of the concrete and formed a more durable concrete. This improvement was attributed to the formation of a high-density WB mixture due to WB [51]. Korkanç and Tuğrul [45] stated that the durability properties of basalts can fulfil the requirement for use as an aggregate for concrete production.

3.5. Water Penetration Test

The water penetration values of the mixtures are given in Figure 8. The maximum 7-day water penetration result was obtained as 21 mm for the control mixture and the minimum was 16 mm for WB100, while the maximum was the 28-day water penetration result obtained as 19 mm for the control mixture and the minimum was 14 mm for the WB100. Therefore, it was determined that there was a 23.8% and 26.3% reduction in the water penetration values for 7 and 28 days, respectively. All mixtures were more impermeable than the control mixture. This condition can be clarified by noting that the density of the WB is higher than the crushed stone [51]. This situation can be also observed in the literature studies. Aja et al. [7] stated that the penetration of concrete with WB satisfied the standards. When the test results were examined, it was determined that the WB used in this study caused a greater decrease in the water penetration value than those of the studies in the literature.

3.6. Relationships between the Properties of Concrete Mixture with WB

The correlation (relationship) of test results is one of the methods frequently used in studies to evaluate experimental data [65]. For this study, the correlation relations between the mechanical and durability properties with the compressive strength at 7 and 28 days are given in Figure 9. In addition, the correlation coefficients (R2) between the mechanical and durability properties with the compressive strength are given in Table 3. The analysis results show that there was a high correlation between the mechanical and durability properties with the compressive strength. Because of this, the R2 was determined as greater than 0.90 for all the relations. All the correlation relations were determined as polynomial. Furthermore, the correlation relations between the durability properties at 7 and 28 days are shown in Figure 10. Furthermore, the correlation coefficients (R2) between the durability properties are given in Table 4. The correlation coefficients pointed out that the durability properties of theconcrete with WB had strong relationships (R2 > 0.95) with each other.

4. Conclusions

In this study, the effect of using WB instead of coarse aggregate on the mechanical and durability properties of standard concrete was investigated and the following results were obtained:
  • When the mechanical properties of the mixtures were considered, the utilization of WB improved the compressive strength of the mixtures. This improvement was approximately 7%, 10% and 15% for WB50, WB75 and WB100 compared to the control mixture, respectively. This increment can be attributed to the high quality and irregular particle shape of WB, and the increase in adhesion between the paste and WB.
  • According to the flexural strength test results, WB enhanced the flexural strength of the mixtures. The flexural strength of WB100 was greater than that of the control mixture in the ratios of 6.40% and 7.20% at 7 and 28 days, respectively. This improvement can be explained by the irregular and elongated shape of WB.
  • When the durability properties of the mixtures were taken into account, the capillary water absorption value reduced depending on the amount of WB. The capillary water absorption values of the control and WB100 were 0.278–0.039 mm/min0.5 and 0.253–0.032 mm/min0.5 for 7 and 28 days, respectively. This result indicates that WB influenced the impermeability of the concrete positively. This situation can be explained by the low void and water absorption values of WB.
  • The rapid chloride permeability test value decreased as the WB increased. The rapid chloride permeability value of WB100 was 35.91% less at 7 days and 24.10% at 28 days, compared to the control mixture. This result shows that WB enhanced the durability properties. This improvement was attributed to the formation of a high-density concrete mixture with WB due to the WB.
  • The water penetration results of the control mixture and WB100 at 7 days were 21 mm and 16 mm, respectively, while the water penetration results of the control mixture and WB100 at 28 days were 19 mm and 14 mm, respectively. These findings show that the concrete mixture with WB was more durable than the control mixture. This condition can be clarified by the fact that the density of the WB is higher than the crushed stone.
  • When the correlation relations were considered, the R2 was determined as higher than 0.90 for the correlation between the mechanical and durability properties with the compressive strength. The correlation relations between the durability properties also had strong relationships with each other (R2 > 0.95).
All the results of this study demonstrated that the utilization of WB instead of coarse aggregate improved the mechanical and durability properties of standard concrete. This utilization (up to 100%) can not only enhance the properties of the concrete, but can also provide more sustainable concrete production.

Author Contributions

Conceptualization, M.D., H.E.Y. and F.Y.; validation, M.D. and H.E.Y.; formal analysis, H.E.Y., M.D. and F.Y.; investigation, M.D., H.E.Y. and F.Y.; writing—original draft preparation, H.E.Y., M.D. and F.Y.; writing—review and editing, M.D., H.E.Y. and F.Y.; supervision, M.D. and H.E.Y.; funding acquisition, H.E.Y. and M.D. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

The authors gratefully acknowledge the support of the research by the project “Pre-implementation Works-Increasing Technology Readiness Level (TRL) Implemented by the Consortium PBŚ, SC PBŚ and SC UEP as part of the “INKUBATOR INNOWACYJNOŚCI 4.0”.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Gencel, O.; Karadag, O.; Oren, O.H.; Bilir, T. Steel Slag and Its Applications in Cement and Concrete Technology: A Review. Constr. Build. Mater. 2021, 283, 122783. [Google Scholar] [CrossRef]
  2. Murari, K.; Siddique, R.; Jain, K.K. Use of Waste Copper Slag, a Sustainable Material. J. Mater. Cycles Waste Manag. 2015, 17, 13–26. [Google Scholar] [CrossRef]
  3. Ali, T.; Iqbal, N.; Ali Khan, M.; Ali, M.; Shahzada, K. Evaluation of Flexure Strength Behavior of Over Burnt Brick Ballast Aggregate Concrete. J. Eng. Res. Appl. 2014, 4, 15–21. [Google Scholar]
  4. Li, V.C.; Horii, H.; Kabele, P.; Kanda, T.; Lim, Y.M. Repair and Retrofit with Engineered Cementitious Composites. Eng. Fract. Mech. 2000, 65, 317–334. [Google Scholar] [CrossRef] [Green Version]
  5. Erdoğan, T.Y. Beton; ODTÜ Geliştirme Vakfı Yayıncılık ve İletişim: Ankara, Turkey, 2007. [Google Scholar]
  6. Habert, G.; Miller, S.A.; John, V.M.; Provis, J.L.; Favier, A.; Horvath, A.; Scrivener, K.L. Environmental Impacts and Decarbonization Strategies in the Cement and Concrete Industries. Nat. Rev. Earth Environ. 2020, 1, 559–573. [Google Scholar] [CrossRef]
  7. Sainz-Aja, J.; Carrascal, I.; Polanco, J.A.; Thomas, C.; Sosa, I.; Casado, J.; Diego, S. Self-Compacting Recycled Aggregate Concrete Using out-of-Service Railway Superstructure Wastes. J. Clean Prod. 2019, 230, 945–955. [Google Scholar] [CrossRef]
  8. Kazmi, S.M.S.; Munir, M.J.; Wu, Y.F. Application of Waste Tire Rubber and Recycled Aggregates in Concrete Products: A New Compression Casting Approach. Resour. Conserv. Recycl. 2021, 167, 105353. [Google Scholar] [CrossRef]
  9. Kaza, S.; Yao, L.C.; Bhada-Tata, P.; van Woerden, F. What a Waste 2.0: A Global Snapshot of Solid Waste Management to 2050; World Bank Publications: Washington, DC, USA, 2018. [Google Scholar] [CrossRef]
  10. Moura, W.A.; Gonçalves, J.P.; Lima, M.B.L. Copper Slag Waste as a Supplementary Cementing Material to Concrete. J. Mater. Sci. 2007, 42, 2226–2230. [Google Scholar] [CrossRef]
  11. Pappu, A.; Saxena, M.; Asolekar, S.R. Solid Wastes Generation in India and Their Recycling Potential in Building Materials. Build. Environ. 2007, 42, 2311–2320. [Google Scholar] [CrossRef]
  12. Kazmi, S.M.S.; Munir, M.J.; Abbas, S.; Saleem, M.A.; Khitab, A.; Rizwan, M. Development of Lighter and Eco-Friendly Burnt Clay Bricks Incorporating Sugarcane Bagasse Ash. Pak. J. Eng. Appl. Sci. 2017, 21, 1–5. [Google Scholar]
  13. Munir, M.J.; Abbas, S.; Nehdi, M.L.; Kazmi, S.M.S.; Khitab, A. Development of Eco-Friendly Fired Clay Bricks Incorporating Recycled Marble Powder. J. Mater. Civ. Eng. 2018, 30, 04018069. [Google Scholar] [CrossRef]
  14. García, S.Y.; Gaya, C.G. Reusing Discarded Ballast Waste in Ecological Cements. Materials 2019, 12, 3887. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  15. Oficemen Homepage. Available online: www.oficemen.com (accessed on 27 December 2022).
  16. Bajželj, B.; Allwood, J.M.; Cullen, J.M. Designing Climate Change Mitigation Plans That Add Up. Environ. Sci. Technol. 2013, 47, 8062–8069. [Google Scholar] [CrossRef]
  17. Dasari, N.; Jogi, S.; Daripalli, V.B.; Suryawanshi, P. Comparative Analysis of Concrete Strength Against Recyclable Ballast and Granite Scrap as Partial Replacement of Coarse Aggregate. Int. J. Progress. Res. Sci. Eng. 2020, 1, 36–41. [Google Scholar]
  18. Sainz-Aja, J.; Thomas, C.; Carrascal, I.; Polanco, J.A.; de Brito, J. Fast Fatigue Method for Self-Compacting Recycled Aggregate Concrete Characterization. J. Clean. Prod. 2020, 277, 123263. [Google Scholar] [CrossRef]
  19. Sainz-Aja, J.A.; Carrascal, I.A.; Polanco, J.A.; Sosa, I.; Thomas, C.; Casado, J.; Diego, S. Determination of the Optimum Amount of Superplasticizer Additive for Self-Compacting Concrete. Appl. Sci. 2020, 10, 3096. [Google Scholar] [CrossRef]
  20. Sainz-Aja, J.; Pombo, J.; Tholken, D.; Carrascal, I.; Polanco, J.; Ferreño, D.; Casado, J.; Diego, S.; Perez, A.; Filho, J.E.A.; et al. Dynamic Calibration of Slab Track Models for Railway Applications Using Full-Scale Testing. Comput. Struct. 2020, 228, 106180. [Google Scholar] [CrossRef]
  21. Ray, S.; Haque, M.; Soumic, S.A.; Mita, A.F.; Rahman, M.M.; Tanmoy, B.B. Use of Ceramic Wastes as Aggregates in Concrete Production: A Review. J. Build. Eng. 2021, 43, 102567. [Google Scholar] [CrossRef]
  22. Aprianti, E.; Shafigh, P.; Bahri, S.; Farahani, J.N. Supplementary Cementitious Materials Origin from Agricultural Wastes—A Review. Constr. Build. Mater. 2015, 74, 176–187. [Google Scholar] [CrossRef] [Green Version]
  23. Meyer, C. The Greening of the Concrete Industry. Cem. Concr. Compos. 2009, 31, 601–605. [Google Scholar] [CrossRef]
  24. Kumar Mehta, P.; Monteiro, P.J.M. Concrete: Microstructure, Properties, and Materials, 4th ed.; McGraw Hill: New York, NY, USA, 2017. [Google Scholar]
  25. Aslam, M.; Shafigh, P.; Jumaat, M.Z. Oil-Palm by-Products as Lightweight Aggregate in Concrete Mixture: A Review. J. Clean. Prod. 2016, 126, 56–73. [Google Scholar] [CrossRef]
  26. Shafigh, P.; Jumaat, M.Z.; Mahmud, H.b.; Alengaram, U.J. Oil Palm Shell Lightweight Concrete Containing High Volume Ground Granulated Blast Furnace Slag. Constr. Build. Mater. 2013, 40, 231–238. [Google Scholar] [CrossRef]
  27. Mo, K.H.; Thomas, B.S.; Yap, S.P.; Abutaha, F.; Tan, C.G. Viability of Agricultural Wastes as Substitute of Natural Aggregate in Concrete: A Review on the Durability-Related Properties. J. Clean Prod. 2020, 275, 123062. [Google Scholar] [CrossRef]
  28. Mohammed, S.I.; Najim, K.B. Mechanical Strength, Flexural Behavior and Fracture Energy of Recycled Concrete Aggregate Self-Compacting Concrete. Structures 2020, 23, 34–43. [Google Scholar] [CrossRef]
  29. Kozioł, W.; Ciepliński, A.; Machniak, Ł.; Borcz, A. Kruszywa w Budownictwie. Cz. 1. Kruszywa Naturalne. Nowocz. Bud. Inżynieryjne 2015, 4, 98–100. Available online: http://www.nbi.com.pl/assets/NBI-pdf/2015/4_61_2015/pdf/31_Kruszywa_naturalne.pdf (accessed on 27 December 2022).
  30. Collivignarelli, M.C.; Cillari, G.; Ricciardi, P.; Miino, M.C.; Torretta, V.; Rada, E.C.; Abbà, A. The Production of Sustainable Concrete with the Use of Alternative Aggregates: A Review. Sustainability 2020, 12, 7903. [Google Scholar] [CrossRef]
  31. Dong, Q.; Wang, G.; Chen, X.; Tan, J.; Gu, X. Recycling of Steel Slag Aggregate in Portland Cement Concrete: An Overview. J. Clean. Prod. 2021, 282, 124447. [Google Scholar] [CrossRef]
  32. International Energy Agency (IEA). United States—Policies and Legislation. Available online: http://www.ieahev.org/by-country/united-states-policy-and-legislation/ (accessed on 27 December 2022).
  33. Han, J.; Thakur, J.K. Sustainable Roadway Construction Using Recycled Aggregates with Geosynthetics. Sustain. Cities Soc. 2015, 14, 342–350. [Google Scholar] [CrossRef]
  34. Dutkiewicz, M.; Yücel, H.E.; Yıldızhan, F. Evaluation of the Performance of Different Types of Fibrous Concretes Produced by Using Wollastonite. Materials 2022, 15, 6904. [Google Scholar] [CrossRef]
  35. Yücel, H.E.; Dutkiewicz, M.; Yıldızhan, F. Application of ECC as a Repair/Retrofit and Pavement/Bridge Deck Material for Sustainable Structures: A Review. Materials 2022, 15, 8752. [Google Scholar] [CrossRef]
  36. Tam, V.W.Y.; Soomro, M.; Evangelista, A.C.J. A Review of Recycled Aggregate in Concrete Applications (2000–2017). Constr. Build. Mater. 2018, 172, 272–292. [Google Scholar] [CrossRef]
  37. Kim, K.; Shin, M.; Cha, S. Combined Effects of Recycled Aggregate and Fly Ash towards Concrete Sustainability. Constr. Build. Mater. 2013, 48, 499–507. [Google Scholar] [CrossRef]
  38. Debieb, F.; Courard, L.; Kenai, S.; Degeimbre, R. Mechanical and Durability Properties of Concrete Using Contaminated Recycled Aggregates. Cem. Concr. Compos. 2010, 32, 421–426. [Google Scholar] [CrossRef]
  39. Rao, A.; Jha, K.N.; Misra, S. Use of Aggregates from Recycled Construction and Demolition Waste in Concrete. Resour. Conserv. Recycl. 2007, 50, 71–81. [Google Scholar] [CrossRef]
  40. Indraratna, B.; Qi, Y.; Malisetty, R.S.; Navaratnarajah, S.K.; Mehmood, F.; Tawk, M. Recycled Materials in Railroad Substructure: An Energy Perspective. Railw. Eng. Sci. 2022, 30, 304–322. [Google Scholar] [CrossRef]
  41. Hussain, A.; Hussaini, S.K.K. Use of Steel Slag as Railway Ballast: A Review. Transp. Geotech. 2022, 35, 100779. [Google Scholar] [CrossRef]
  42. Singh, R.P.; Nimbalkar, S.; Singh, S.; Choudhury, D. Field Assessment of Railway Ballast Degradation and Mitigation Using Geotextile. Geotext. Geomembr. 2020, 48, 275–283. [Google Scholar] [CrossRef]
  43. Guo, Y.; Xie, J.; Fan, Z.; Markine, V.; Connolly, D.P.; Jing, G. Railway Ballast Material Selection and Evaluation: A Review. Constr. Build. Mater. 2022, 344, 128218. [Google Scholar] [CrossRef]
  44. Bilgiç, Ş. Demiryolu. 2017, pp. 1–42. Available online: https://scholar.google.com.tr/citations?view_op=view_citation&hl=tr&user=OqvynFEAAAAJ&citation_for_view=OqvynFEAAAAJ:aqlVkmm33-oC (accessed on 28 December 2022).
  45. Korkanç, M.; Tuǧrul, A. Evaluation of Selected Basalts from Nǐde, Turkey, as Source of Concrete Aggregate. Eng. Geol. 2004, 75, 291–307. [Google Scholar] [CrossRef]
  46. Sainz-Aja, J.; Carrascal, I.; Polanco, J.A.; Thomas, C. Fatigue Failure Micromechanisms in Recycled Aggregate Mortar by ΜCT Analysis. J. Build. Eng. 2020, 28, 101027. [Google Scholar] [CrossRef]
  47. Lee, S.; Jang, S.Y.; Kim, C.Y.; Ahn, E.J.; Kim, S.P.; Gwon, S.; Shin, M. Effects of Redispersible Polymer Powder on Mechanical and Durability Properties of Preplaced Aggregate Concrete with Recycled Railway Ballast. Int. J. Concr. Struct. Mater. 2018, 12, 69. [Google Scholar] [CrossRef] [Green Version]
  48. Kuşkapan, E.; Çodur, M.K.; Çodur, M.Y. Türkiye’deki Demiryolu Enerji Tüketiminin Yapay Sinir Ağları ile Tahmin Edilmesi. Konya Mühendislik Bilim. Derg. 2022, 10, 72–84. [Google Scholar] [CrossRef]
  49. Kozak, M.; Bölge, T. Demiryolu Balastının ve Özelliklerinin Araştırılması. Demiryolu Mühendisliği 2021, 13, 86–96. [Google Scholar] [CrossRef]
  50. Shibuya, A.; Iyoda, T. A Review of Preplaced-Aggregate Concrete Using Recycled Aggregate and Railway Wasted Ballast. Lect. Notes Civ. Eng. 2021, 101, 1979–1988. [Google Scholar] [CrossRef]
  51. Choi, H.-B.; Park, J.-O.; Kim, T.-H.; Lee, K.-R.; Choi, C.; Park, H.-B.; Kim, J.-O.; Lee, T.-H.; Mechanical, K.-R.; Agrela, F. Mechanical Properties of Basalt-Based Recycled Aggregate Concrete for Jeju Island. Materials 2021, 14, 5429. [Google Scholar] [CrossRef]
  52. Raif Boğa, A.; Şenol, A.F. The Effect of Waste Marble and Basalt Aggregates on the Fresh and Hardened Properties of High Strength Self-Compacting Concrete. Constr. Build. Mater. 2023, 363, 129715. [Google Scholar] [CrossRef]
  53. Al-Baijat, H.M. The Use of Basalt Aggregates in Concrete Mixes in Jordan. Jordan J. Civ. Eng. 2008, 2, 63. [Google Scholar]
  54. American Society for Testing and Materials. Committee C-1 on Cement. Standard Test Method for Compressive Strength of Hydraulic Cement Mortars; ASTM International: West Conshohocken, PA, USA, 2013. [Google Scholar]
  55. C78/C78M-18; Standard Test Method for Flexural Strength of Concrete Using Simple Beam with Third-Point Loading. ASTM International: West Conshohocken, PA, USA, 2018.
  56. ASTM C1585-04; Standard Test Method for Measurement of Rate of Absorption of Water by Hydraulic-Cement Concretes. ASTM International: West Conshohocken, PA, USA, 2007.
  57. ASTM C 1202; Standard Test Method for Electrical Indication of Concrete’s Ability to Resist Chloride Penetration. Annual Book of ASTM Standards. American Society of Testing and Materials: West Conshohocken, PA, USA, 2009.
  58. BS EN 12390-8; Testing Hardened Concrete. Depth of Penetration of Water Under Pressure. European Standards: London, UK, 2000.
  59. Tabsh, S.W.; Abdelfatah, A.S. Influence of Recycled Concrete Aggregates on Strength Properties of Concrete. Constr. Build. Mater. 2009, 23, 1163–1167. [Google Scholar] [CrossRef]
  60. Özturan, T.; Çeçen, C. Effect of Coarse Aggregate Type on Mechanical Properties of Concretes with Different Strengths. Cem. Concr. Res. 1997, 27, 165–170. [Google Scholar] [CrossRef]
  61. Siva Kishore, I.; Mounika, L.; Prasad, C.M.; Krishna, B.H. Experimental Study on the Use of Basalt Aggregate in Concrete Mixes. SSRG Int. J. Civ. Eng. 2015, 2, 39–42. [Google Scholar] [CrossRef]
  62. Ajdukiewicz, A.; Kliszczewicz, A. Influence of Recycled Aggregates on Mechanical Properties of HS/HPC. Cem. Concr. Compos. 2002, 24, 269–279. [Google Scholar] [CrossRef]
  63. Karasin, A.; Hadzima-Nyarko, M.; Işık, E.; Doğruyol, M.; Karasin, I.B.; Czarnecki, S. The Effect of Basalt Aggregates and Mineral Admixtures on the Mechanical Properties of Concrete Exposed to Sulphate Attacks. Materials 2022, 15, 1581. [Google Scholar] [CrossRef] [PubMed]
  64. Pek, N.A. Use of Basalt Aggregate in Concrete Marine Structures. J. Turk. Chamb. Civ. Eng. 2014, 422, 6849–6866. [Google Scholar]
  65. Yücel, H.E.; Öz, H.Ö.; Güneş, M. The Effects of Acidic and Basic Pumice on Physico-Mechanical and Durability Properties of Self-Compacting Concretes. Green Build. Constr. Econ. 2020, 1, 21–36. [Google Scholar] [CrossRef]
Figure 1. Particle size distribution of aggregate.
Figure 1. Particle size distribution of aggregate.
Materials 16 02665 g001
Figure 2. (a) Natural sand, (b) Crushed stone and (c) WB.
Figure 2. (a) Natural sand, (b) Crushed stone and (c) WB.
Materials 16 02665 g002
Figure 3. (a) Compressive, (b) flexural, (c) capillary water absorption, (d) rapid chloride permeability and (e) water penetration test setups.
Figure 3. (a) Compressive, (b) flexural, (c) capillary water absorption, (d) rapid chloride permeability and (e) water penetration test setups.
Materials 16 02665 g003aMaterials 16 02665 g003b
Figure 4. Compressive strength of mixtures.
Figure 4. Compressive strength of mixtures.
Materials 16 02665 g004
Figure 5. Flexural strength of mixtures.
Figure 5. Flexural strength of mixtures.
Materials 16 02665 g005
Figure 6. Capillary water absorption of mixtures.
Figure 6. Capillary water absorption of mixtures.
Materials 16 02665 g006
Figure 7. Rapid chloride permeability of mixtures.
Figure 7. Rapid chloride permeability of mixtures.
Materials 16 02665 g007
Figure 8. Water penetration of mixtures.
Figure 8. Water penetration of mixtures.
Materials 16 02665 g008
Figure 9. Correlation relations between mechanical and durability properties with compressive strength.
Figure 9. Correlation relations between mechanical and durability properties with compressive strength.
Materials 16 02665 g009aMaterials 16 02665 g009b
Figure 10. Correlation relations between durability properties.
Figure 10. Correlation relations between durability properties.
Materials 16 02665 g010
Table 1. Chemical composition and physical properties of Portland cement.
Table 1. Chemical composition and physical properties of Portland cement.
Chemical Composition (%)Portland Cement
CaO62.19
SiO219.83
Al2O35.31
Fe2O33.17
MgO1.89
SO33.27
K2O1.01
Na2O0.21
Physical properties
Loss of Ignition2.98
Specific Gravity3.15
Fineness (Blaine) (m2/kg)326
Table 2. Mix design of concrete (kg/m3).
Table 2. Mix design of concrete (kg/m3).
MaterialsControlWB50WB75WB100
Cement486.96486.96486.96486.96
Coarse Aggregate955.41477.71238.85-
Fine Aggregate625.72625.72625.72625.72
WB Aggregate-477.71716.56955.41
Water236.66236.66236.66236.66
Slump Value (mm)180178177177
Table 3. Correlation coefficients between mechanical and durability properties with compressive strength.
Table 3. Correlation coefficients between mechanical and durability properties with compressive strength.
PropertiesCompressive Strength
(R2)
7 Days
(R2)
28 Days
Flexural Strength0.98190.9945
Capillary Water Absorption0.99980.9875
Rapid Chloride Permeability0.99610.9217
Water Penetration0.99790.9439
Table 4. Correlation coefficients between durability properties.
Table 4. Correlation coefficients between durability properties.
PropertiesCapillary Water AbsorptionRapid Chloride PermeabilityWater Penetration
(R2)
7 Days
(R2)
7 Days
(R2)
7 Days
(R2)
28 Days
(R2)
28 Days
(R2)
28 Days
Capillary Water Absorption110.99860.9490.99940.9842
Rapid Chloride Permeability0.99860.949110.99641
Water Penetration0.99940.98420.9964111
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Yücel, H.E.; Dutkiewicz, M.; Yıldızhan, F. The Effect of Waste Ballast Aggregates on Mechanical and Durability Properties of Standard Concrete. Materials 2023, 16, 2665. https://doi.org/10.3390/ma16072665

AMA Style

Yücel HE, Dutkiewicz M, Yıldızhan F. The Effect of Waste Ballast Aggregates on Mechanical and Durability Properties of Standard Concrete. Materials. 2023; 16(7):2665. https://doi.org/10.3390/ma16072665

Chicago/Turabian Style

Yücel, Hasan Erhan, Maciej Dutkiewicz, and Fatih Yıldızhan. 2023. "The Effect of Waste Ballast Aggregates on Mechanical and Durability Properties of Standard Concrete" Materials 16, no. 7: 2665. https://doi.org/10.3390/ma16072665

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