1. INTRODUCTION
⌅The
building industry is among the biggest consumers of natural resources.
This sector is considered to cause a great environmental impact, and for
generates enormous quantities of waste that reaches landfills. The
different wastes are generated during the construction of civil works
such as roads, bridges and housing and during the demolition of
infrastructure and buildings, when they have reached the end of their
useful life, or for reasons of remodeling (1-31.
Duan, P.; Song, L.; Yan, C.; Ren, D.; Li, Z. (2017) Novel thermal
insulating and lightweight composites from metakaolin geopolymer and
polystyrene particles. Ceram. Int. 43 [6], 5115-5120. https://doi.org/10.1016/j.ceramint.2017.01.025.
2.
Domínguez, A.; Domínguez, M.I.; Ivanova, S.; Centeno, M.A.; Odriozola,
J.A. (2016) Recycling of construction and demolition waste generated by
building infrastructure for the production of glassy materials. Ceram. Int. 42 [14], 15217-15223. https://doi.org/10.1016/j.ceramint.2016.06.157.
3.
Aghdam, K.A.; Rad, A.F.; Shakeri, H.; Sardroud, J.M. (2018) Approaching
green buildings using eco-efficient construction materials: a review of
the state-of-the-art. J. Constr. Eng. Proj. Manag. 8 [3], 1-23. https://doi.org/10.6106/JCEPM.2018.8.3.001.
).
Approximately 10 billion tons of CDW, it is estimated, are generated
worldwide each year. Of this, the United States contributes
approximately 700 million tons, China around 2.3 billion tons, and the European Union more than 800 million tons (44.
Wu, H.; Zuo, J.; Zillante, G.; Wang, J.; Yuan, H. (2019) Status quo and
future directions of construction and demolition waste research: A
critical review. J. Clean. Prod. 240, 118163. https://doi.org/10.1016/j.jclepro.2019.118163.
).
Every year, it is estimated 615 million tons of CDW is generated around
the world, illegal dumping is the most economical alternative makes the
dumping of constructions and demolitions debris along streets, and
river is not an uncommon sight (55.
Akhtar, A.; Sarmah, A.K. (2018) Construction and demolition waste
generation and properties of recycled aggregate concrete: A global
perspective. J. Clean. Prod. 186, 262-281.
).
The CDW occupies 12% of the world’s municipal solid waste, moreover,
most of CDW waste ends up in landfill, generating the saturation of
landfilled sites, which is responsible for the environment pollution (66.
Wang, X.; Yu, R.; Shui, Z.; Song, Q.; Liu, Z.; Bao, M.; Liu, Z.; Wu, S.
(2019) Optimized treatment of recycled construction and demolition
waste in developing sustainable ultra-high performance concrete. J. Clean. Prod. 221, 805-816. https://doi.org/10.1016/j.jclepro.2019.02.201.
).
The CDW are materials of great interest because of their large volume
generated worldwide and because the levels of use do not reach 30%
globally and the waste minimization strategies are generally based on
the reduction, reuse and recycle to reduce the volume of CDW generated
every year around the world (77.
Vincent, T.; Guy, M.; Louis-César, P.; Jean-François, B.; Richard, M.
(2022) Physical process to sort construction and demolition waste
(C&DW) fines components using process water. Waste Manag. 143, 125-134. https://doi.org/10.1016/j.wasman.2022.02.012.
).
The capacity to reuse and recycle CDW depends on the feasibility to
sort the different components and to ensure their competitiveness with
new materials, in respect to residual contamination and production
costs. Important efforts have been deployed over the last decades to
identify, develop and implement efficient recycling processes as
screening, magnetic separation, manual sorting, optical sorting,
crushing and separation of lightweight material by air classification,
and design of and mobile plant design to facilitate mobility and lower
processing costs (7-107.
Vincent, T.; Guy, M.; Louis-César, P.; Jean-François, B.; Richard, M.
(2022) Physical process to sort construction and demolition waste
(C&DW) fines components using process water. Waste Manag. 143, 125-134. https://doi.org/10.1016/j.wasman.2022.02.012.
8.
3RMCDQ. (2017) Évaluation des alternatives de valorisation des résidus
de criblage fin issus des centres de tri des débris de construction, de
rénovation et de démolition. Quebec. Retrieved from www.3rmcdq.qc.ca.
9. Reciclados Industriales. Bogotá. (2019) Retrieved from https://recicladosindustriales.co/.
10. Ecotech, G. CDW Disposal System GEPECOTECH. (2022). Retrieved from https://www.gepecotech.com/solution/construction-demolition-waste-system.html?utm_source=google&utm_medium=g&utm_campaign=cdwaste&utm_content=649540851337&utm_term=demolition_waste
recycling&match=p&item=&target=kwd-3920165559&device=c&gclid=CjwKCAjwiOCgB.
).
In general, for Latin American countries - Colombia included - the
problem with CDW generation can be attributed to inefficient use and the
lack of suitable policies for handling and managing CDW. The different
sectors of society must therefore direct efforts towards searching for
comprehensive solutions, amongst which Circular Economy strategies can
be put forward in the construction sector that encompass the entire life
cycle of materials, making use of the concepts of Industrial Ecology
such as Industrial Symbiosis and By-product Synergy, so that the waste
from the construction industry becomes the raw material of this sector
or of other industrial sectors (33.
Aghdam, K.A.; Rad, A.F.; Shakeri, H.; Sardroud, J.M. (2018) Approaching
green buildings using eco-efficient construction materials: a review of
the state-of-the-art. J. Constr. Eng. Proj. Manag. 8 [3], 1-23. https://doi.org/10.6106/JCEPM.2018.8.3.001.
).
Although it is estimated recycled aggregate could save natural sources
and reduce environmental pollution, its inferior quality compared to
virgin ones, such as low density, high porosity, high water absorption
rate, and micro-cracks in ITZ (1111.
Şimşek, O.; Pourghadri H.; Gökçe, H.S. (2022) Performance of fly
ash-blended Portland cement concrete developed by using fine or coarse
recycled concrete aggregate. Constr. Build. Mater. 357, 129431. https://doi.org/10.1016/j.conbuildmat.2022.129431.
).
Nevertheless, mortars produced with recycled aggregate from CDW have
obtained adequate physical and mechanical properties, due to the
adequate distribution of the grain size and to the greater content of
fines present (1212.
Ferreira, R.L.S.; Anjos, M.A.S.; Ledesma, E.F.; Pereira, J.E.S. and
Nóbrega, A.K.C. (2020) Evaluation of the physical-mechanical properties
of cement-lime based masonry mortars produced with mixed recycled
aggregates. Mater. Constr. 70 [337], e210. https://doi.org/10.3989/mc.2020.02819.
).
As such, in recent years, research has been carried out on
incorporating recycled aggregates from CDW for mortars and concrete.
Recycled coarse aggregate dosage in conventional or high-performance
concrete, producing good quality construction materials at a reasonable
cost and with a lower environmental impact (1313.
López Ruiz, L.A.; Roca Ramón, X.; Gassó Domingo, S. (2020) The circular
economy in the construction and demolition waste sector - A review and
an integrative model approach. J. Clean. Prod. 248, 119238. https://doi.org/10.1016/j.jclepro.2019.119238.
, 1414. Kumar, G.; Shrivastava, S.; Gupta, R.C. (2020) Paver blocks manufactured from construction & demolition waste. Mater. Today Proc. 27, 311-317. https://doi.org/10.1016/j.matpr.2019.11.039.
).
Different researchers have found the recycled aggregates have a highwater absorption rate (1515.
Garg, N.; Shrivastava, S. (2022) A review on utilization of recycled
concrete aggregates (RCA) and ceramic fines in mortar application. Mater. Today Proc. 73, 64-73. https://doi.org/10.1016/j.matpr.2022.09.226.
)
which causes the free water in the mortar mix to be absorbed by the
recycled aggregates. The data shows that as the percent recycled
aggregates fines increases in mortar, the consistency decreases linearly
(1515.
Garg, N.; Shrivastava, S. (2022) A review on utilization of recycled
concrete aggregates (RCA) and ceramic fines in mortar application. Mater. Today Proc. 73, 64-73. https://doi.org/10.1016/j.matpr.2022.09.226.
).
Specifically, rendering mortars elaborated with CDW have shown presence
of cracking due to capillary stresses, these can be controlled by
reduce the fines content, the grain size distribution, and the effective
water/cement ratio (1616.
Miranda, L.F.R.; Selmo, S.M.S. (2006) CDW recycled aggregate
renderings: Part I - Analysis of the effect of materials finer than 75
μm on mortar properties. Constr. Build. Mater. 20 [9], 615-624. https://doi.org/10.1016/j.conbuildmat.2005.02.025.
).
Particle size distribution and shape of CDW greatly influence the ratio
of voids within the mortar, thus conditioning its performance (1212.
Ferreira, R.L.S.; Anjos, M.A.S.; Ledesma, E.F.; Pereira, J.E.S. and
Nóbrega, A.K.C. (2020) Evaluation of the physical-mechanical properties
of cement-lime based masonry mortars produced with mixed recycled
aggregates. Mater. Constr. 70 [337], e210. https://doi.org/10.3989/mc.2020.02819.
). As the void ratio decreases so less binder and water is required to make a mortar, and then shrinkage also decreases (1717. Braga, M.; Brito, J.; Veiga, R. (2012) Incorporation of fine concrete aggregates in mortars. Constr. Build. Mater. 36, 960-968. https://doi.org/10.1016/j.conbuildmat.2012.06.031.
).
On the case of concrete elaborate with red clay brick wastes, a higher
water absorption and porosity, reflected in changes in the consistency
of the concrete (1818.
Silva, R.V.; Brito, J.; Dhir, R.K. (2016) Performance of cementitious
renderings and masonry mortars containing recycled aggregates from
construction and demolition wastes. Constr. Build. Mater. 105, 400-415. https://doi.org/10.1016/j.conbuildmat.2015.12.171.
).
Incorporation of fine recycled aggregates and CDW powder has been
evaluated, finding improvements in mechanical properties with the
incorporation of fine concrete aggregates (< 0.149 mm) (1919.
Jesus, S.; Maia, C.; Brazão Farinha, C.; Brito, J.; Veiga, R. (2019)
Rendering mortars with incorporation of very fine aggregates from
construction and demolition waste. Constr. Build. Mater. 229, 116844. https://doi.org/10.1016/j.conbuildmat.2019.116844.
) and mixed recycled aggregate powders (2020.
Ferreira, R.L.S.; Anjos, M.A.S.; Nóbrega, A.K.C.; Pereira, J.E.S.;
Ledesma, E.F. (2019) The role of powder content of the recycled
aggregates of CDW in the behaviour of rendering mortars Constr. Build. Mater. 208, 601-612. https://doi.org/10.1016/j.conbuildmat.2019.03.058.
).
Nevertheless, the physical, mechanical, and durability properties of
newly produced concrete are significantly affected by many properties of
recycled, such as amount, compressive strength, abrasion resistance,
water absorption, density, size, particle size distribution, and shape (1111.
Şimşek, O.; Pourghadri H.; Gökçe, H.S. (2022) Performance of fly
ash-blended Portland cement concrete developed by using fine or coarse
recycled concrete aggregate. Constr. Build. Mater. 357, 129431. https://doi.org/10.1016/j.conbuildmat.2022.129431.
).
The
non-stone-derived wastes that are most difficult to manage, on
completing their useful life, expanded polystyrene (EPS) features
prominently, unlike other plastics, it is challenging to get back in its
base form. The recycling process required to reform foam blocks, and
the entire process is time-consuming and expensive, thus, the majority
of commercial and curbside waste management companies require its
disposal in the trash can, and finally in landfills due to its low
density and high air content (95%) (2121. Deer, R. (2021) Styrofoam an environmental problem? RoadRunner. Retrieved from https://www.roadrunnerwm.com/blog/styrofoam-problems-and-how-to-help#:~:text=Most
recycling facilities are unable is time-consuming and expensive.
).
According to Environmental Protections Agency (EPA), in 2018 in USA
14.5 million tons of plastic container and packaging were generated, and
over 69% was landfilled (2222. EPA. (2022) Containers and packaging United States Environmental Protection Agency. Retrieved from https://www.epa.gov/facts-and-figures-about-materials-waste-and-recycling/containers-and-packaging-product-specific.
).
The problem associated with its generation is that it fulfills its
industrial function very quickly and soon ends up as part of the
accumulation of solid waste (2121. Deer, R. (2021) Styrofoam an environmental problem? RoadRunner. Retrieved from https://www.roadrunnerwm.com/blog/styrofoam-problems-and-how-to-help#:~:text=Most
recycling facilities are unable is time-consuming and expensive.
, 2323.
Cácerres, M.A.; Sánchez, M.; Soto, M.; Maspoch, L.; Sánchez Hernández,
M.; Sánchez Rojo, A. (2015) Desarrollo de un proceso de reciclaje para
la fracción mixta de residuos de plástico, provenientes de plantas de
separación selectiva. in II Congrés UPC Sostenible. Retrieved from https://upcommons.upc.edu/handle/2099/8207?show=full.
). It is also chemically inert and a non-biodegradable material (2424. World centric for a better world (2019) Impacts and risks of polystyrene. https://www.worldcentric.com/journal/impacts-and-risks-of-styrofoam.
).
On the other hand, improving the energy efficiency of machinery and
premises is one of the most important ways of achieving global energy
sustainability. Energy that is not used is the cheapest energy of all,
and buildings are large consumer of thermal energy. In fact, the
residential and services sectors account for 27% of the total energy
consumed in the Europe Union, and much of this energy is used in air
conditioning (2525.
Morales, M.P.; Muñoz, P.; Juárez, M.C.; Mendívil, M.A.; Olasolo, P.
(2016). Influence of the type of lightweight clay brick on the
equivalent thermal transmittance of different types of façades on
buildings. Mater. Construcc. 66 [323], e096. https://doi.org/10.3989/mc.2016.08115.
). Lightweight materials have been used to improve the thermal efficiency, the incorporating of low-density clay bricks (2525.
Morales, M.P.; Muñoz, P.; Juárez, M.C.; Mendívil, M.A.; Olasolo, P.
(2016). Influence of the type of lightweight clay brick on the
equivalent thermal transmittance of different types of façades on
buildings. Mater. Construcc. 66 [323], e096. https://doi.org/10.3989/mc.2016.08115.
), vermiculite particles (2626.
Gencel, O.; Coz Diaz, J.J.; Stcu, M.; Koksal, F.; Alvarez, F.P.;
Martinez-Barrera, G.; Brostow, W. (2014) Properties of gypsum composites
containing vermiculite and polypropylene fibers: Numerical and
experimental results. Energy Build. 70, 135-144. https://doi.org/10.1016/j.enbuild.2013.11.047.
, 2727.
Binici, H.; Aksogan, O.; Dıncer, A.; Luga, E.; Eken, M.; Isikaltun, O.
(2020) The possibility of vermiculite, sunflower stalk and wheat stalk
using for thermal insulation material production. Therm. Sci. Eng. Prog. 18 [21], 100567. https://doi.org/10.1016/j.tsep.2020.100567.
) and EPS-based composites showed improvement in acoustic and thermal insulation (2121. Deer, R. (2021) Styrofoam an environmental problem? RoadRunner. Retrieved from https://www.roadrunnerwm.com/blog/styrofoam-problems-and-how-to-help#:~:text=Most
recycling facilities are unable is time-consuming and expensive.
, 28-3028.
Fernández, D.; Yedra, E.; Morón, C.; Zaragoza, A.; Kosior-Kazberuk, M.
(2022) Circular building process: reuse of insulators from construction
and demolition waste to produce lime mortars. Buildings. 12 [2], 220. https://doi.org/10.3390/buildings12020220.
29.
Villaquirán-Caicedo, M.A.; Perea, V.N.; Ruiz, J.E.; Mejía de Gutiérrez,
R. (2022) Mechanical, physical and thermoacoustic properties of
lightweight composite geopolymers Propiedades mecánicas, físicas y
termoacústicas de geopolímeros compuestos aligerados. Ingen. Compet. 24 [1], 1-21
30.
Oliveira, K.A.; Oliveira, C.A.B.; Molina, J.C. (2021) Lightweight
recycled gypsum with residues of expanded polystyrene and cellulose
fiber to improve thermal properties of gypsum. Mater. Construcc. 71 [341], e242. https://doi.org/10.3989/mc.2021.07520.
). However, there is not reports about utilization of EPS residues together CDW for preparation of render mortar.
This research reported the results of producing an interior render mortar made from mixtures of other of wastes - red clay brick, concrete demolition as fine aggregates and sanded EPS - and evaluated the influence of incorporating waste materials on the mechanical, thermal, physical, and acoustic properties, to obtain a sustainability composite material that offers greater living comfort to interior homes, while contributing to the circular economy.
2. EXPERIMENTAL METHODOLOGY
⌅2.1. Starting materials
⌅General use Portland cement was used, the CDW used in this research were selected and sampled from the waste storage yard of MAECOL®, Materiales Ecológicos de Colombia SAS, located in Yumbo, Colombia. The materials came from various work in building in the city of Cali. Specifically, fired red clay brick waste (BW) and mortar and concrete waste (MW) were used, which underwent crushing in a jaw mill followed by milling in a hammer mill. The resulting material (Figure 1) was sifted through a No. 30 mesh sieve, and the retained material was used for this research.
Expanded polystyrene (EPS) waste was selected and samples taken from a building site in the city of Cali (Constructora Bolívar, Colombia). The EPS was collected in the form of blocks and was used in forming slab caissons. The EPS was sanded in an industrial sander (Trofemarcas, Colombia) at a speed of 330 m/min and with a No. 60 sandpaper. The sanded EPS was sieved in a No. 50 mesh sieve, and the retained material used for this study.
2.2. Tests and characterization techniques
⌅The following characterization techniques were used:
-
The particle size distribution of the raw materials was determined by laser particle size analyzer (Mastersizer 2000, Malvern Panalytical). The density and absorption of fine aggregates BW and MW was testing according to ASTM C128. In the case of sanded EPS residue, the “Unit Weight” was determined with a graduated cylinder, which was filled to a volume of 54 ml, then the sanded EPS was weighed. Observation of the particle morphology and optimized mixing with CDW-EPS was carried out in a JEOL scanning electron microscope (SEM), Ref: JSM-6490LV, high vacuum (3x10-6 torr) and accelerating voltage at 20 kV. The equipment has an INCAPentaFETx3 Model 7573 detector (Oxford Instruments). Additionally, the EDS analysis unit was used to determine the semi-quantitative chemical composition of the materials evaluated. The powder raw materials and pieces resulting from the compressive strength test were metalized in a Denton Vacuum Desk IV tank on a gold plate which was deposited for later observation.
-
Compressive strength was evaluated at 7 and 28 days, using a Tinius Olsen testing machine with a capacity of 50 kN at a test speed of 1 mm/min, under the ASTM C109/C109M-10 standard. For each mix, three specimens were tested, according to the standard method.
-
Adherence was evaluated at 28 days, using the same universal testing machine, by adapting the ASTM C932 standard method. For each mix, six specimens were tested; in this test, the mortars designed with waste materials were adhered to a mortar consisting of cement:sand in a 1:3 ratio, liquid/solid ratio of 0.26, whose compressive strength is 17.7 MPa.
-
Apparent density, water absorption, and permeable pore volume percentage were evaluated according to the ASTM C642 standard method.
-
Setting time was evaluated using the Vicat Apparatus. This test was performed following Colombian technical standard NTC118. The drying time of optimized mortars was determined comparatively on applying it to an interior brick wall of the laboratory. Initial dry time is when the material is applied in a first coat until the second coat can be used. The feel of the applicator determines this time. The final drying time is the time interval from when the last layer of material is applied until the cloth is completely dry to the touch.
-
The test to determine the conductivity, thermal diffusivity and specific heat of the mixes was carried out in the Hot Disk Thermal Constant Analyzer, model TPS 500 S, following the ISO 22007-2 standard. For this test, cubic geometry samples of 50 mm x 50 mm x 15 mm were used.
-
The measurement of acoustic properties test was carried out following the recommendations of other authors (31-3331. Fraile-Garcia, E.; Ferreiro-Cabello, J.; Defez, B.; Peris-Fajanes, G. (2016) Acoustic behavior of hollow blocks and bricks made of concrete doped with waste-tire rubber. Mater. 9 [12], 962. https://doi.org/10.3390/ma9120962.
32. Holmes, N.; Browne, A; Montague, C. (2014) Acoustic properties of concrete panels with crumb rubber as a fine aggregate replacement. Constr. Build. Mater. 73, 195-204. https://doi.org/10.1016/j.conbuildmat.2014.09.107.
33. Orrego Gonzáles, A.; Ealo Cuello, J.L.; Pazos Ospina, J.F. (2018) Low-cost and easily implemented anechoic acoustic chambers. Sci. Tech. 23 [4], 471-478.
) as an alternative method to the impedance tube. An Alexis model M1520 active monitor was used as a frequency emission source. A Beyedynamic microphone, model MM1, with condenser and omnidirectional polar pattern was used, with a measurement range between 50 Hz and 16,000 Hz. The Solid State Logic interface model SSL2+ and the Smaart V8 software were employed.
Additionally, application of the optimal mixes was carried out on the surface of a wall to determine the characteristics of material consumption, workability during application, drying time and finally visual monitoring was carried out up to 60 days after application.
3. RESULTS AND ANALYSIS
⌅3.1. Raw materials
⌅Figure 2 shows the particle size distribution curves for the waste used, BW, MW and EPS. The average particle size for BW and MW was 322.2 µm and 222.3 µm, respectively, and in the case of EPS it was 385.4 µm. The density of Portland cement is provided by the manufacturer technical data sheet, which is 2411 Kg/m3. The apparent density was 2550 Kg/m3 and 1870 Kg/m3 for BW and MW respectively; and the absorption was 2.11% for BW, and 12.35% for MW. The “Unit Weight” for EPS sanded was 140 Kg/m3.
The Figure 3 presents the SEM images for the waste materials under study. The MW powders (Figure 3a and b)
are composed of particles of irregular shapes and different sizes, some
less than 100 µm, which corroborates what was found in the laser
granulometry for this waste. Also observed in Figure 4a is the presence of cement paste with many micropores adhered to
large-sized particles. Other studies have shown that a higher content of
adhered mortar influences a greater water absorption and a decrease in
the density (34-3634.
Ferreira, R.L.S.; Anjos, M.A.S.; Maia, C.; Pinto, L.; Azevedo, A.R.;
Brito, J. (2021) Long-term analysis of the physical properties of the
mixed recycled aggregate and their effect on the properties of mortars. Constr. Build. Mater. 274, 121796. https://doi.org/10.1016/j.conbuildmat.2020.121796.
35.
Bonifazi, G.; Palmieri, R; Serranti, S. (2018) Evaluation of attached
mortar on recycled concrete aggregates by hyperspectral imaging. Constr. Build. Mater. 169, 835-842. https://doi.org/10.1016/j.conbuildmat.2018.03.048.
36.
Kim, J. (2022) Influence of quality of recycled aggregates on the
mechanical properties of recycled aggregate concretes: An overview. Constr. Build. Mater. 328, 127071. https://doi.org/10.1016/j.conbuildmat.2022.127071.
). In Figure 3c and d,
the BW powders are shown. These are made up of angular and irregular
particles of different sizes, corroborating the broad size distribution
previously shown in the Figure 3a. For higher increases in the BW particle (Figure 5d),
it is possible to observe an irregular and vitreous surface of the
particles due to brick firing temperatures around 800-900 °C.
The lightweight EPS filler, after the sanding process, presented a wrinkled and/or rolled plate-like morphology (Figure 3e and f), which can be attributed to the sanding process at high revolutions. The higher magnification image (Figure 3f) shows that the wall of the initial foam has been modified and after sanding, crushing of the cells was generated. The EDS results indicated in Figure 3b and 3d are shown in Table 1, corroborating the aluminum-silicate nature for BW and MW.
BW | Element | Point 1 (wt %) | Point 2 (wt %) |
O | 29.46 | 20.81 | |
Al | 17.76 | 19.07 | |
Si | 37.52 | 28.16 | |
Fe | 15.25 | 31.96 | |
MW | Element | Point 1 (wt %) | Point 2 (wt %) |
O | 36.53 | 42.36 | |
Si | 11.38 | 15.45 | |
Ca | 36.19 | 42.19 | |
Fe | 8.15 | ||
Br | 7.75 |
3.2. Mix design
⌅The render mortars were made from 70% by volume recycled fine aggregates (BW, MW and EPS) and 30% by volume matrix (99.7 wt% general use Portland cement and 0.30 wt% methyl hydroxyethyl cellulose powder (CellueastTM FM ME 40000) for improving the workability of plaster when applied on a wall. The matrix content remained fixed, and within the 70% that constitutes aggregates, different combinations were used following the EPS/CDW volume proportionality of 70/30 (mix A1), 50/50 (mixes A4, A5 and A6) and 30/70 (mixes A7, A8 and A9) for a total of 7 mixes (Figure 4 and Table 2). Additionally, as a commercial render mortar from IMPADOC® was used, labelled AC1.
Component | A1 | A4 | A5 | A6 | A7 | A8 | A9 |
---|---|---|---|---|---|---|---|
Cement, (Kg) | 299.1 | 299.1 | 299.1 | 299.1 | 299.1 | 299.1 | 299.1 |
CellueastTM, (Kg) | 0.9 | 0.9 | 0.9 | 0.9 | 0.9 | 0.9 | 0.9 |
EPS, (Kg) | 68.6 | 49 | 49 | 49 | 29.4 | 29.4 | 29.4 |
BW, (Kg) | 267.75 | 446.25 | 267.75 | 624.75 | 624.75 | 274.85 | 874.75 |
MW, (Kg) | 196.35 | 327.25 | 458.15 | 196.35 | 458.15 | 641.41 | 274.89 |
Water
content was adjusted to achieve a constant workability among all mixes,
which was similar to that required during the application of the
commercial render mortar AC1. The total water to cement ratio (w/c) for
the mortars was defined as that required for obtaining a consistency
(measured on flow table) similar to AC1 (94 mm). Table 3 shows the water content needed for each mix. The high-water requirement
is related to the morphology (pronounced angularity), higher absorption
and more porous surface for recycled aggregates particles after the
crushing process (1818.
Silva, R.V.; Brito, J.; Dhir, R.K. (2016) Performance of cementitious
renderings and masonry mortars containing recycled aggregates from
construction and demolition wastes. Constr. Build. Mater. 105, 400-415. https://doi.org/10.1016/j.conbuildmat.2015.12.171.
)
which will be observed later in the microscopy images. Previously, has
been reported that mortar with EPS required a higher content of mixing (2828.
Fernández, D.; Yedra, E.; Morón, C.; Zaragoza, A.; Kosior-Kazberuk, M.
(2022) Circular building process: reuse of insulators from construction
and demolition waste to produce lime mortars. Buildings. 12 [2], 220. https://doi.org/10.3390/buildings12020220.
).
In general, the high-water requirement in the mixes caused a slow
setting process, which led to the decision to leave the mixes hardening
at ambient laboratory conditions (relative humidity 70%, temperature 25
°C).
Mix ID | A1 | A4 | A5 | A6 | A7 | A8 | A9 | AC1 |
---|---|---|---|---|---|---|---|---|
(%vol. EPS) | 49 | 35 | 35 | 35 | 21 | 21 | 21 | 0 |
solid: water (parts by weight) |
1: 1.58 | 1: 0.97 | 1: 0.88 | 1: 1.01 | 1: 0.63 | 1: 0.56 | 1: 0.60 | 1: 0.45 |
3.3. Mechanical and physical performance of the render mortars produced
⌅In Figure 5a,
the compressive strength results for the proposed mixes are shown. The
UNE EN 998-1-2018 standard classifies the render mortar according to
compressive strength at 28 days (CS), and water capillary (W). The
mortar for interior render application, do not required permeable
specification (W0), and compressive strength must be: CS I (0.4-2.5
MPa), CS II (1.5-5.0 MPa), CS III (3.5-7.5 MPa), CS IV (> = 6 MPa).
Mixes A1, A5 and A6 did not reach the minimum value of 0.4 MPa
contemplated in the standard to be classified as an interior render
mortar. In those mixtures, the results show that increasing the EPS
content directly affects the mechanical properties of the mix, due to
the strength close to zero of the EPS particles and their high
compressibility. Different authors have shown that, on using EPS,
microcracks are generated in the interfacial transition zone (ITZ)
between the aggregate particles and the cement paste, further weakening
the mixes (11.
Duan, P.; Song, L.; Yan, C.; Ren, D.; Li, Z. (2017) Novel thermal
insulating and lightweight composites from metakaolin geopolymer and
polystyrene particles. Ceram. Int. 43 [6], 5115-5120. https://doi.org/10.1016/j.ceramint.2017.01.025.
, 3737.
Sayadi, A.A.; Tapia, J.V.; Neitzert, T.R.; Clifton, G.C. (2016) Effects
of expanded polystyrene (EPS) particles on fire resistance, thermal
conductivity and compressive strength of foamed concrete. Constr. Build. Mater. 112, 716-724. https://doi.org/10.1016/j.conbuildmat.2016.02.218.
).
It is important to clarify that other researchers have produced render
mortars with compressive strengths between 2.5-14.5 MPa using different
percentages of recycled aggregates (1616.
Miranda, L.F.R.; Selmo, S.M.S. (2006) CDW recycled aggregate
renderings: Part I - Analysis of the effect of materials finer than 75
μm on mortar properties. Constr. Build. Mater. 20 [9], 615-624. https://doi.org/10.1016/j.conbuildmat.2005.02.025.
, 1818.
Silva, R.V.; Brito, J.; Dhir, R.K. (2016) Performance of cementitious
renderings and masonry mortars containing recycled aggregates from
construction and demolition wastes. Constr. Build. Mater. 105, 400-415. https://doi.org/10.1016/j.conbuildmat.2015.12.171.
, 2828.
Fernández, D.; Yedra, E.; Morón, C.; Zaragoza, A.; Kosior-Kazberuk, M.
(2022) Circular building process: reuse of insulators from construction
and demolition waste to produce lime mortars. Buildings. 12 [2], 220. https://doi.org/10.3390/buildings12020220.
) employing EPS-recycled filler can achieve compressive strength between 2.3-2.9 MPa for hydraulic lime mortars.
The
A4 mortar (with the same total proportion of BW and MW) gave the
highest compressive strength (0.48 MPa) from 35% EPS group. Similarly,
for the group of mixes with 21% EPS (A7, A8, A9), the A7 mortar was
found to have the highest compressive strength (1 MPa); like A4, it has
the same proportion of BW and MW waste in its composition. These results
can be explained: (i) via a better balance in the particle size
distributions, exhibited increased packing, where the MW waste
contributes a greater amount of fine particles with d (0.5) = 69.1 µm,
while the brick waste BW provides coarser particles with d (0.5) = 197
µm, similar results have been shown previously (1818.
Silva, R.V.; Brito, J.; Dhir, R.K. (2016) Performance of cementitious
renderings and masonry mortars containing recycled aggregates from
construction and demolition wastes. Constr. Build. Mater. 105, 400-415. https://doi.org/10.1016/j.conbuildmat.2015.12.171.
).
Also, (ii) the equal distribution in volume between the BW and MW
wastes in the A4 and A7 mixes; the finest fraction of the BW could also
be contributing pozzolanic activity, by reacting with the portlandite
from OPC hydration process of the matrix, a behavior that has been
previously reported (1818.
Silva, R.V.; Brito, J.; Dhir, R.K. (2016) Performance of cementitious
renderings and masonry mortars containing recycled aggregates from
construction and demolition wastes. Constr. Build. Mater. 105, 400-415. https://doi.org/10.1016/j.conbuildmat.2015.12.171.
, 3838.
Zawrah, M.F.; Gado, R.A.; Feltin, N.; Ducourtieux, S.; Devoille, L.
(2016) Recycling and utilization assessment of waste fired clay bricks
(Grog) with granulated blast-furnace slag for geopolymer production. Process Saf. Environ. Prot. 103, 237-251. https://doi.org/10.1016/j.psep.2016.08.001.
).
Nevertheless, the compressive strength results for the mixes proposed
in this study were lower than for the commercial sample, AC1 (3.05 MPa).
In general, the strength of the mortars decreases up to 50% with the
replacement of the aggregate due to the high absorption capacity in
mixtures with recycled aggregates (2020.
Ferreira, R.L.S.; Anjos, M.A.S.; Nóbrega, A.K.C.; Pereira, J.E.S.;
Ledesma, E.F. (2019) The role of powder content of the recycled
aggregates of CDW in the behaviour of rendering mortars Constr. Build. Mater. 208, 601-612. https://doi.org/10.1016/j.conbuildmat.2019.03.058.
, 3939.
Fernández-Ledesma, E.; Jiménez, J.R.; Ayuso, J.; Corinaldesi, V.;
Iglesias-Godino, F.J. (2016) A proposal for the maximum use of recycled
concrete sand in masonry mortar design. Mater. Construcc. 66 [321], e075. https://doi.org/10.3989/mc.2016.08414.
, 4040.
Fernández-Ledesma, E.; Jiménez, J.R.; Ayuso, J.; Fernández, J.M.;
Brito, J. (2015) Maximum feasible use of recycled sand from construction
and demolition waste for eco-mortar production - Part-I: Ceramic
masonry waste. J. Clean. Prod. 87 [1], 692-706. https://doi.org/10.1016/j.jclepro.2014.10.084.
). Additionally, the values of compressive strength in this study are similar to values for EPS-gypsum composites (3030.
Oliveira, K.A.; Oliveira, C.A.B.; Molina, J.C. (2021) Lightweight
recycled gypsum with residues of expanded polystyrene and cellulose
fiber to improve thermal properties of gypsum. Mater. Construcc. 71 [341], e242. https://doi.org/10.3989/mc.2021.07520.
, 4141.
Bumanis, G.; Pavils, P.; Sahmenko, G.; Mironovs, D.; Rucevskis, S.;
Korjakins, A.; Bajare, D. (2023) Thermal and sound insulation properties
of recycled expanded polystyrene granule and gypsum composites. Recycling. 8 [1], 19. https://doi.org/10.3390/recycling8010019.
), and vermiculite-gypsum composites (2626.
Gencel, O.; Coz Diaz, J.J.; Stcu, M.; Koksal, F.; Alvarez, F.P.;
Martinez-Barrera, G.; Brostow, W. (2014) Properties of gypsum composites
containing vermiculite and polypropylene fibers: Numerical and
experimental results. Energy Build. 70, 135-144. https://doi.org/10.1016/j.enbuild.2013.11.047.
), and higher than vermiculite-gypsum-sunflower stalk fiber composites (2727.
Binici, H.; Aksogan, O.; Dıncer, A.; Luga, E.; Eken, M.; Isikaltun, O.
(2020) The possibility of vermiculite, sunflower stalk and wheat stalk
using for thermal insulation material production. Therm. Sci. Eng. Prog. 18 [21], 100567. https://doi.org/10.1016/j.tsep.2020.100567.
).
The results of adherence test for mixtures is shown in Figure 5b.
Mixes A4, A5 and A6 with EPS content of 35% had a lower adherence
compared to A7, A8, A9 (21% EPS), which indicates that there is an
inverse proportional relationship between the EPS content in the mix and
the adhesive strength the material can acquire once applied. It can
also be seen that the adhesive values change markedly in the group of
mixes A7, A8, and A9, depending on the variation in the content of BW
and MW wastes, adhesive strength found to be greater in A7 (equal
volumes of BW and MW waste), followed by mix A9 (a higher volume of MW)
compared to mix A8. Just as was explained previously, by eliminating the
fine material adhered to the coarse particle, this could contribute to
the improved performance in adhesive strength. Adhesive strength values
of 0.25 to 0.7 MPa have been found in render mortar by utilization of
recycled sand (16-1816.
Miranda, L.F.R.; Selmo, S.M.S. (2006) CDW recycled aggregate
renderings: Part I - Analysis of the effect of materials finer than 75
μm on mortar properties. Constr. Build. Mater. 20 [9], 615-624. https://doi.org/10.1016/j.conbuildmat.2005.02.025.
17. Braga, M.; Brito, J.; Veiga, R. (2012) Incorporation of fine concrete aggregates in mortars. Constr. Build. Mater. 36, 960-968. https://doi.org/10.1016/j.conbuildmat.2012.06.031.
18.
Silva, R.V.; Brito, J.; Dhir, R.K. (2016) Performance of cementitious
renderings and masonry mortars containing recycled aggregates from
construction and demolition wastes. Constr. Build. Mater. 105, 400-415. https://doi.org/10.1016/j.conbuildmat.2015.12.171.
, 4040.
Fernández-Ledesma, E.; Jiménez, J.R.; Ayuso, J.; Fernández, J.M.;
Brito, J. (2015) Maximum feasible use of recycled sand from construction
and demolition waste for eco-mortar production - Part-I: Ceramic
masonry waste. J. Clean. Prod. 87 [1], 692-706. https://doi.org/10.1016/j.jclepro.2014.10.084.
, 4242.
Saiz Martínez, P.; González Cortina, M.; Fernández Martínez, F.;
Rodríguez Sánchez, A. (2016). Comparative study of three types of fine
recycled aggregates from construction and demolition waste (CDW), and
their use in masonry mortar fabrication. J. Clean. Prod. 118, 162-169. https://doi.org/10.1016/j.jclepro.2016.01.059.
). (1717. Braga, M.; Brito, J.; Veiga, R. (2012) Incorporation of fine concrete aggregates in mortars. Constr. Build. Mater. 36, 960-968. https://doi.org/10.1016/j.conbuildmat.2012.06.031.
) and (2020.
Ferreira, R.L.S.; Anjos, M.A.S.; Nóbrega, A.K.C.; Pereira, J.E.S.;
Ledesma, E.F. (2019) The role of powder content of the recycled
aggregates of CDW in the behaviour of rendering mortars Constr. Build. Mater. 208, 601-612. https://doi.org/10.1016/j.conbuildmat.2019.03.058.
)
have found that the use of CDW with an average size smaller than 150 µm
increases the shrinkage in mortars by 44% compared to that in mortars
made with natural aggregates, and this increases their cracking,
affecting the mechanical strength. These results follow other previous
studies where the adherence strength between 0.13-0.23 MPa employing
EPS-recycled filler (2828.
Fernández, D.; Yedra, E.; Morón, C.; Zaragoza, A.; Kosior-Kazberuk, M.
(2022) Circular building process: reuse of insulators from construction
and demolition waste to produce lime mortars. Buildings. 12 [2], 220. https://doi.org/10.3390/buildings12020220.
).
From the above, it is concluded that the higher the EPS content in the
mix, the lower the mechanical properties, in agreement with various
authors (11.
Duan, P.; Song, L.; Yan, C.; Ren, D.; Li, Z. (2017) Novel thermal
insulating and lightweight composites from metakaolin geopolymer and
polystyrene particles. Ceram. Int. 43 [6], 5115-5120. https://doi.org/10.1016/j.ceramint.2017.01.025.
, 3737.
Sayadi, A.A.; Tapia, J.V.; Neitzert, T.R.; Clifton, G.C. (2016) Effects
of expanded polystyrene (EPS) particles on fire resistance, thermal
conductivity and compressive strength of foamed concrete. Constr. Build. Mater. 112, 716-724. https://doi.org/10.1016/j.conbuildmat.2016.02.218.
). From ANOVA (Table 4)
analysis for adherence test show differences between the mixtures. The
ANOVA concludes that there is significant evidence that every mixtures
influences the levels of adherence. This is how the contrasts showed
differences in the combinations of A4-A7, A4-A8, A4-A9, A7-A8, and A7-A9
mixtures-opposite case between mixes A8 and A9. Mixes A7, A8 and A9
presented the most outstanding results, reaching values between 0.044
and 0.085 MPa. The Figure 6.
shows specimens A6, A7 and AC1 after the adhesive test. The A6 mixture
had an adhesive mode failure, indicating little adhesion between the
render mixture and the substrate. While the A7 mixture had a cohesive
mode failure, indicating that the render mixture had satisfactory
adhesion to the substrate. AC1 has a mixed type failed.
Source | P Adj. | Std. Error | Pr ( > |t| ) | |
---|---|---|---|---|
A4-A7 | 0.00005 | 0.0051 | 3.71E-06 | Significance |
A4-A8 | 0.02850 | 0.0051 | 0.000329 | |
A4-A9 | 0.00599 | 0.0089 | 0.177398 | |
A7-A8 | 0.00139 | 0.0051 | 0.401374 | |
A7-A9 | 0.00550 | |||
A8-A9 | 0.65216 | No significance | ||
Degrees of freedom | 8 | Pure Error | 0.009 | |
t value | 31.76 | Residual error | 0.008851 |
3.4. Density, water absorption, and porosity properties
⌅The
low density, higher angularity, and surface roughness of recycled
aggregate particles compared to natural crushed ones play an important
role in reducing the density and poorer workability of concrete mixtures
(1111.
Şimşek, O.; Pourghadri H.; Gökçe, H.S. (2022) Performance of fly
ash-blended Portland cement concrete developed by using fine or coarse
recycled concrete aggregate. Constr. Build. Mater. 357, 129431. https://doi.org/10.1016/j.conbuildmat.2022.129431.
, 1515.
Garg, N.; Shrivastava, S. (2022) A review on utilization of recycled
concrete aggregates (RCA) and ceramic fines in mortar application. Mater. Today Proc. 73, 64-73. https://doi.org/10.1016/j.matpr.2022.09.226.
, 3535.
Bonifazi, G.; Palmieri, R; Serranti, S. (2018) Evaluation of attached
mortar on recycled concrete aggregates by hyperspectral imaging. Constr. Build. Mater. 169, 835-842. https://doi.org/10.1016/j.conbuildmat.2018.03.048.
). The results of density, water absorption and porosity are shown in Table 5.
The high-water absorption of the mortars under study stands out,
reaching values between 56.2% and 103.5%. A directly proportional
relationship was found between the increase in EPS content and water
absorption. High water absorption and high porosity in recycled
aggregates results in a significant decrease in compressive strength in
mortars, as previously has been observed (2020.
Ferreira, R.L.S.; Anjos, M.A.S.; Nóbrega, A.K.C.; Pereira, J.E.S.;
Ledesma, E.F. (2019) The role of powder content of the recycled
aggregates of CDW in the behaviour of rendering mortars Constr. Build. Mater. 208, 601-612. https://doi.org/10.1016/j.conbuildmat.2019.03.058.
, 4343.
Patra, I.; Al-Awsi, G.R.L.; Hasan, Y.M.; Almotlaq, S.S.K. (2022)
Mechanical properties of concrete containing recycled aggregate from
construction waste. Sustain. Energy Technol. Assessments. 53, 102722. https://doi.org/10.1016/j.seta.2022.102722.
).
The group of mixes A4, A5, A6 thus had a greater absorption compared to
mixes A7, A8, A9. The porosity in the mixes was higher to the extent
that the EPS, MW and BW waste (highly porous waste) was incorporated,
which is associated with different phenomena such as: (i) the greater
demand for water in the mixes (Table 3)
to achieve adequate workability (as explained in the Methodology
section) as the EPS was increased. Moreover, as is known, the water that
does not react with the OPC matrix is finally released during drying,
leaving behind porosity, which in turn is reflected in the greater
water absorption for the mixes with 35% EPS compared to the samples with
21%EPS. In addition, it is possible that during the test, the water was
trapped inside the channels of the EPS waste, which were observed to be
deep and flattened (SEM, Figure 3e and 3f), and inside the pores of the recycled MW and BW aggregates (Figure 3 a, b, c, d), phenomena that have been reported by other authors (1919.
Jesus, S.; Maia, C.; Brazão Farinha, C.; Brito, J.; Veiga, R. (2019)
Rendering mortars with incorporation of very fine aggregates from
construction and demolition waste. Constr. Build. Mater. 229, 116844. https://doi.org/10.1016/j.conbuildmat.2019.116844.
, 2020.
Ferreira, R.L.S.; Anjos, M.A.S.; Nóbrega, A.K.C.; Pereira, J.E.S.;
Ledesma, E.F. (2019) The role of powder content of the recycled
aggregates of CDW in the behaviour of rendering mortars Constr. Build. Mater. 208, 601-612. https://doi.org/10.1016/j.conbuildmat.2019.03.058.
).
Finally, the higher the EPS content, the lower the density of the
mixes, and in all cases the density was lower than that of commercial
AC1.
Mix (%EPS) | A1 | A4 (35%) | A5 (35%) | A6 (35%) | A7 (21%) | A8 (21%) | A9 (21%) | AC1 |
---|---|---|---|---|---|---|---|---|
Permeable pores (%) | 64.75 | 53.93 | 53.75 | 57.97 | 52.01 | 52.71 | 48.90 | 45.45 |
Water absorption (%) | 115.64 | 90.70 | 92.70 | 103.48 | 63.66 | 56.20 | 59.67 | 32.25 |
Apparent density (Kg/m3) | 1240 | 1380 | 1350 | 1430 | 1770 | 1920 | 1590 | 2420 |
The densities of mixes A4, A5, A6 are close to the density of water (1000 Kg/m3),
and during the test they initially floated in water, similar to that
reported by materials based on gypsum. For a render mortar, a low
density can become a technical advantage, since it gives less weight to
the packed material, which favors transport, workability, as well as a
possible lower consumption of material compared to traditional mortars,
which is discussed later in Section 3.8. (1515.
Garg, N.; Shrivastava, S. (2022) A review on utilization of recycled
concrete aggregates (RCA) and ceramic fines in mortar application. Mater. Today Proc. 73, 64-73. https://doi.org/10.1016/j.matpr.2022.09.226.
, 4040.
Fernández-Ledesma, E.; Jiménez, J.R.; Ayuso, J.; Fernández, J.M.;
Brito, J. (2015) Maximum feasible use of recycled sand from construction
and demolition waste for eco-mortar production - Part-I: Ceramic
masonry waste. J. Clean. Prod. 87 [1], 692-706. https://doi.org/10.1016/j.jclepro.2014.10.084.
)
have found a linear fall of the density of hardened mortar as the
replacement ratio of recycled sand increased, which was due to the lower
density of recycled aggregate. The density values are lower than
EPS-lime mortars (2828.
Fernández, D.; Yedra, E.; Morón, C.; Zaragoza, A.; Kosior-Kazberuk, M.
(2022) Circular building process: reuse of insulators from construction
and demolition waste to produce lime mortars. Buildings. 12 [2], 220. https://doi.org/10.3390/buildings12020220.
) and similar to EPS-plaster mortar (4444.
Fernández, D.; Álvarez, M.; Saiz, P.; Zaragoza, A. (2022) Experimental
study with plaster mortars made with recycled aggregate and thermal
insulation residues for application in building. Sustain. 14 [4], 2386. https://doi.org/10.3390/su14042386.
).
According to the previous results of mechanical and physical properties, mixes A4, A7, and A9 were selected for the next part of the study to determine their thermal and acoustic properties.
3.5. Microstructure
⌅The
A7 mortar presented the best results in terms of mechanical properties,
which indicates a better internal cohesion between the aggregates that
compose it and the cement matrix. In Figure 7a an EPS particle can be seen adhered to the mortar, and in Figure 7b the interface between the EPS particle and the cement paste can be
seen, indicating that it is of good quality, dense, without presence of
microcracks, and in this study the anchoring mechanical type is favored
owing to the morphology of the EPS particle. This is in contrast with
other studies in which, when EPS with rounded morphology and sizes from
2.0 mm were used, a weak interface and the appearance of microcracks
were reported (11.
Duan, P.; Song, L.; Yan, C.; Ren, D.; Li, Z. (2017) Novel thermal
insulating and lightweight composites from metakaolin geopolymer and
polystyrene particles. Ceram. Int. 43 [6], 5115-5120. https://doi.org/10.1016/j.ceramint.2017.01.025.
, 2929.
Villaquirán-Caicedo, M.A.; Perea, V.N.; Ruiz, J.E.; Mejía de Gutiérrez,
R. (2022) Mechanical, physical and thermoacoustic properties of
lightweight composite geopolymers Propiedades mecánicas, físicas y
termoacústicas de geopolímeros compuestos aligerados. Ingen. Compet. 24 [1], 1-21
, 3737.
Sayadi, A.A.; Tapia, J.V.; Neitzert, T.R.; Clifton, G.C. (2016) Effects
of expanded polystyrene (EPS) particles on fire resistance, thermal
conductivity and compressive strength of foamed concrete. Constr. Build. Mater. 112, 716-724. https://doi.org/10.1016/j.conbuildmat.2016.02.218.
).
In this investigation, a quality and dense interface was found,
associated with the fineness, and elongated morphology that the EPS
particles retained after mechanical polishing. The mechanical anchoring
of the EPS particle to the matrix, added to the use of a polymer-based
additive, to improve adherence and dispersion in the formulation, allows
a better anchoring of the EPS.
Table 6 shows the chemical composition results by EDS for mix A7 according to the position were EDS analyses were carried out in Figure 7b. The EDS for point 1 and 2, correspond to the elements that constitute the compounds formed in the hydration of the cement and its reaction with the compounds of silica, aluminum and iron present in the waste of mainly ceramic origin (SiO2, Al2O3, and Fe2O3), which upon contact with calcium hydroxides (Portlandite, Ca(OH)2), a product of cement hydration, form compounds such as calcium silicate hydrates (CSH) and calcium aluminates (C3A). In point 3, meanwhile, located between the junction of the EPS particle and the matrix, the constituent elements are C, O and Ca, which indicates the presence of portlandite, and also the carbon from the EPS.
Element | Point 1 (% by weight) | Point 2 (% by weight) | Point 3 (% by weight) |
---|---|---|---|
C | 9.15 | 12.46 | 43.80 |
O | 41.97 | 53.51 | 42.10 |
Al | 8.00 | 1.71 | |
Si | 11.29 | 9.81 | |
Ca | 22.35 | 20.73 | 14.11 |
Fe | 7.25 | 1.79 | |
Identification | Gel CSH | Gel CSH | EPS |
Assessment of the physical and mechanical properties made it possible to define mixes A4, A7 and A9 as optimal. The A7 mix was selected for having the best mechanical properties. In the adherence test, however, no significant differences were found between mixes A8 and A9, which both have 21% EPS content. Mix A9 was therefore selected from these two mixes, which had slightly better performance in mechanical properties. Mix A4 was considered for the next stage due to its high content of EPS (35%), which is expected to favor thermal and acoustic performance.
3.6. Thermal properties
⌅Since the EPS has low conductivity (0.030 W/m·K) (4444.
Fernández, D.; Álvarez, M.; Saiz, P.; Zaragoza, A. (2022) Experimental
study with plaster mortars made with recycled aggregate and thermal
insulation residues for application in building. Sustain. 14 [4], 2386. https://doi.org/10.3390/su14042386.
), it is to be expected that render mortars with higher EPS proportion will have the lowest thermal conductivity. Table 7 presents the results of thermal conductivity, where the proposed mixes
A4, A7, A9 had a lower thermal conductivity than commercial mix AC1. In
turn, as expected, mix A4 (35% EPS) was found to have the lowest
conductivity values. On comparing the conductivity values of the
proposed mixes with AC1, a decrease in this property was found of 79.5%,
62.3% and 71.7% for A4, A7 and A9 respectively. Mixes A4 and A9 gave
lower thermal conductivity when compared to other thermal insulating
materials with EPS particles (2828.
Fernández, D.; Yedra, E.; Morón, C.; Zaragoza, A.; Kosior-Kazberuk, M.
(2022) Circular building process: reuse of insulators from construction
and demolition waste to produce lime mortars. Buildings. 12 [2], 220. https://doi.org/10.3390/buildings12020220.
, 2929.
Villaquirán-Caicedo, M.A.; Perea, V.N.; Ruiz, J.E.; Mejía de Gutiérrez,
R. (2022) Mechanical, physical and thermoacoustic properties of
lightweight composite geopolymers Propiedades mecánicas, físicas y
termoacústicas de geopolímeros compuestos aligerados. Ingen. Compet. 24 [1], 1-21
, 4444.
Fernández, D.; Álvarez, M.; Saiz, P.; Zaragoza, A. (2022) Experimental
study with plaster mortars made with recycled aggregate and thermal
insulation residues for application in building. Sustain. 14 [4], 2386. https://doi.org/10.3390/su14042386.
, 4545.
Villaquirán-Caicedo, M.A.; Mejía de Gutierrez, R.; Sulekar, S.; Davis,
C.; Nino, J. (2015) Thermal properties of novel binary geopolymers based
on metakaolin and alternative silica sources Appl. Clay Sci. 118, 276-282. https://doi.org/10.1016/j.clay.2015.10.005.
). The thermal conductivity in this research are similar to EPS-gypsum composites 0.18-0.24 W/m·K (3030.
Oliveira, K.A.; Oliveira, C.A.B.; Molina, J.C. (2021) Lightweight
recycled gypsum with residues of expanded polystyrene and cellulose
fiber to improve thermal properties of gypsum. Mater. Construcc. 71 [341], e242. https://doi.org/10.3989/mc.2021.07520.
, 4141.
Bumanis, G.; Pavils, P.; Sahmenko, G.; Mironovs, D.; Rucevskis, S.;
Korjakins, A.; Bajare, D. (2023) Thermal and sound insulation properties
of recycled expanded polystyrene granule and gypsum composites. Recycling. 8 [1], 19. https://doi.org/10.3390/recycling8010019.
), vermiculite-gypsum composites-sunflower stalk composites (2727.
Binici, H.; Aksogan, O.; Dıncer, A.; Luga, E.; Eken, M.; Isikaltun, O.
(2020) The possibility of vermiculite, sunflower stalk and wheat stalk
using for thermal insulation material production. Therm. Sci. Eng. Prog. 18 [21], 100567. https://doi.org/10.1016/j.tsep.2020.100567.
); and is lower than mortar elaborate with vermiculite-gypsum (2626.
Gencel, O.; Coz Diaz, J.J.; Stcu, M.; Koksal, F.; Alvarez, F.P.;
Martinez-Barrera, G.; Brostow, W. (2014) Properties of gypsum composites
containing vermiculite and polypropylene fibers: Numerical and
experimental results. Energy Build. 70, 135-144. https://doi.org/10.1016/j.enbuild.2013.11.047.
), 100% glass particles wastes (0.5 W/m·K) and recycled concrete aggregate (0.9-1.3 W/m·K) (4646.
Chindaprasirt, P. (2022) Thermal insulating and fire resistance
performances of geopolymer mortar containing auto glass waste as fine
aggregate. J. Build. Eng. 60, 105178. https://doi.org/10.1016/j.jobe.2022.105178.
).
Mortar | Thermal conductivity (W/m·K) | Reduction vs. commercial AC1 (%) | Volumetric specific heat (MJ/m3.K) | Thermal diffusivity (mm2/s) | Specific heat (J/kg·K) | Thermal inertia (J/m2 s1/2 ·K) |
---|---|---|---|---|---|---|
A4 | 0.1213 ± 0.0184 | 79.5 | 0.7208 | 0.1880 ± 0.0227 | 655.82 ± 0.0611 | 296 |
A7 | 0.2226 ± 0.0123 | 62.3 | 0.9851 | 0.2277 ± 0.0299 | 536.40 ± 0.0917 | 468 |
A9 | 0.1672 ± 0.0013 | 71.7 | 1.0404 | 0.1616 ± 0.0133 | 520.52 ± 0.0977 | 417 |
AC1 | 0.5912 ± 0.0365 | -- | 1.2610 | 0.4706 ± 0.0345 | 522.90 ± 0.0936 | 863 |
It was found that the selected mixes A4, A7 and A9 have a lower specific heat than commercial mix AC1, which means that in the proposed mixes a lower supply of heat energy is required to increase their temperature. The higher specific heat of the A4 mix compared to the other mixes is directly related to the higher content of EPS in the mix, since this has a higher specific heat than natural or recycled aggregates, which in turn allowed a lower thermal conductivity in A4. However, the heat transfer through the thickness of the material is slower in the proposed mixes than in AC1, due to the lower thermal diffusivity of the produced mixes, A9 being the one with the lowest thermal diffusion among the proposed mixes, which is related to the low density of the mix. The proposed mixes have a lower thermal inertia compared to mortar AC1, which indicates that their temperature can increase faster on the surface during an outbreak of fire. However, when compared with materials commonly used in interior construction, plasterboard (386 J/m2 s1/2K), cellular concrete (372,7 J/m2 s1/2K), and chipboard (226 J/m2 s1/2K) show close values (47, 48). Based on UNE-EN-998-1 render mortar A4 and A7 could be classified as type T2 (thermal conductivity < 0.2 W/m·K).
Figure 8 correlates the results of thermal conductivity vs apparent density of
the material. A directly proportional relationship can be observed
between the density of the material and the thermal conductivity. As the
density of the material decreases, its thermal conductivity decreases.
This is directly related to a greater volume of pores that the use of
recycled aggregates gives the material, which in turn causes a decrease
in density and greater water absorption. The thermal conductivity in a
ceramic material decreases as its density decreases (4949.
Gregorová, E.; Pabst, W.; Sofer, Z.; Jankovský, O.; Matějíček, J.
(2012) Porous alumina and zirconia ceramics with tailored thermal
conductivity. J. Phys. Conf. Ser. 395, 012022. https://doi.org/10.1088/1742-6596/395/1/012022.
)
therefore, the percentage of water absorption increases, and the pore
volume increases which means a higher content of air that acts as a heat
flow barrier due to its low thermal conductivity (0.026 W/m·K).
3.7. Acoustic properties
⌅ Figure 9a shows the results of sound pressure level (SPL) measurement relative to
full scale (dBFS) for the mixes evaluated and the direct sound source,
for frequencies between 250 - 4000 Hz. It must be made clear that, since
the measurement is recorded relative to full scale (dBFS), the values
are negative. The more the value is increased, this signifies a lower
SPL. It was found in relation to the SPL of the direct sound source, the
greatest reduction was achieved in general for the frequencies of 2000
Hz and 4000 Hz. A significant reduction was achieved for the frequency
of 250 Hz. In contrast, for the frequencies of 500 Hz and 1000 Hz, in
general, the mixes evaluated did not register a significant decrease in
SPL. Figure 9b presents the results for the absorption coefficient of the developed
render mortars. The A9 mix achieved the highest acoustic absorption
coefficient for the frequencies of 250 Hz and 4000 Hz (0.39 and 0.91
respectively), while the A4 and A7 mixes achieved the highest acoustic
absorption coefficient for the frequencies of 500 Hz (0.15 for both) and
2000 Hz (0.74 and 0.75 respectively). Among the proposed mixes, in
general the acoustic absorption coefficient was low for frequencies of
500 Hz and 1000 Hz. In contrast, (2929.
Villaquirán-Caicedo, M.A.; Perea, V.N.; Ruiz, J.E.; Mejía de Gutiérrez,
R. (2022) Mechanical, physical and thermoacoustic properties of
lightweight composite geopolymers Propiedades mecánicas, físicas y
termoacústicas de geopolímeros compuestos aligerados. Ingen. Compet. 24 [1], 1-21
)
reported acoustic absorption coefficients close to 0.7 for frequencies
of 300 at 500 Hz and close to 0.5 for a frequency of 1000 Hz, for a
geopolymeric cement incorporating 4% (weight) EPS with a particle size
of 2.35 mm. In general, the proposed samples had a higher acoustic
absorption coefficient compared to the commercial mix AC1 for
frequencies of 250, 500, 2000 and 4000 Hz. This is related to the higher
permeable pore volume percentage and low density of the proposed mix
samples compared to AC1 (5050.
Moretti, E.; Belloni, E.; Agosti, F. (2016) Innovative mineral fiber
insulation panels for buildings: Thermal and acoustic characterization. Appl. Energy, 169, 421-432. https://doi.org/10.1016/j.apenergy.2016.02.048.
).
In accordance with the classification of the ISO 11654-1997 standard, the proposed mixes have an Absorbent (Class D) behavior for frequencies of 250 Hz, Slightly absorbent (Class E) for 500 Hz, Reflective for 1000 Hz, and Highly absorbent (Class C) for frequencies of 2000 Hz and 4000 Hz. Only for mix A9 is it Extremely absorbent (Class A) for a frequency of 4000 Hz. This can be related to the fact that, at high frequencies, the waveform lengths are smaller, so they can more easily enter the pores of the material, which is why the materials can better absorb sounds.
3.8. Application of render mortars
⌅Application of the proposed mixes A4, A7 and A9 along with the commercial mix AC1 was carried out. In Table 8 the results of the estimated consumption of material to cover a section
on a brick wall of 0.40 m x 0.50 m to two layers approximately 1 mm
thick each are presented (Figure 10). It is known that the lower density contributes to the enhanced workability for the similar consistency of concrete mixtures (1111.
Şimşek, O.; Pourghadri H.; Gökçe, H.S. (2022) Performance of fly
ash-blended Portland cement concrete developed by using fine or coarse
recycled concrete aggregate. Constr. Build. Mater. 357, 129431. https://doi.org/10.1016/j.conbuildmat.2022.129431.
).
It was found that mix A4 had the lowest consumption of material and the
highest demand for water. Mixes A7 and A9 had a similar consumption.
The commercial mix AC1 had a higher consumption and waste of material,
compared to a lower consumption of water. The proposed mixes allow a
reduction in material consumption of at least 51% compared to AC1. This
is associated with the results of the apparent density test, in which it
was shown that the proposed mixes have a lower density than the
commercial mix. In addition, there is a directly proportional
relationship between the apparent density of the material and
consumption during application. The use of EPS waste allows, in addition
to reducing the density of the material, lowering the consumption of
material during application, which constitutes a technical and possibly
economic advantage for the end user of the material, compared to the use
of a traditional render mortar, corroborating what was reported by (2020.
Ferreira, R.L.S.; Anjos, M.A.S.; Nóbrega, A.K.C.; Pereira, J.E.S.;
Ledesma, E.F. (2019) The role of powder content of the recycled
aggregates of CDW in the behaviour of rendering mortars Constr. Build. Mater. 208, 601-612. https://doi.org/10.1016/j.conbuildmat.2019.03.058.
).
Mortar | Solid:water ratio (parts by weight) | Consumption of material (kg/m2/mm thickness) | Reduction in consumption compared to AC1 (%) | Initial drying time (min) | Initial setting time (min) | Final drying time (h) | Final setting time (h) |
---|---|---|---|---|---|---|---|
A4 (35% EPS) | 1: 1.11 | 1.04 | 56% | 40 | 1330.4 | 4 | 50.7 |
A7 (21% EPS) | 1: 0.66 | 1.16 | 51% | 40 | 237.6 | 4 | 27.3 |
A9 (21% EPS) | 1: 0.75 | 1.17 | 51% | 40 | 69.8 | 4 | 28.3 |
AC1 | 1: 0.34 | 2.37 | ---- | 30 | 37.3 | 2 | 3.3 |
From
the proposed mixes, the best workability (lower sliding resistance by
the applicator trowel and better surface quality) during application was
for A9. However, difficulties arose during the dispersion of the mix on
the brick surface. The best workability in mix A9 can be related to the
high MW content in this mix compared to A4 and A7. MW, according to the
results of the particle size distribution, had a bimodal distribution
of particles (Figure 4b),
thus providing a better distribution between the fine and coarse
particles, allowing the finer ones to fill the spaces between the coarse
particles, resulting in better dispersion during application to the
surface. According to Weymouth’s gradation theory, in order to obtain
adequate workability in mortars and concretes, grains of a single size
must have enough space to move within the space left by grains of the
subsequent larger size. When this occurs, the particles can move freely
and are better distributed in the mortar, making it extremely workable (1616.
Miranda, L.F.R.; Selmo, S.M.S. (2006) CDW recycled aggregate
renderings: Part I - Analysis of the effect of materials finer than 75
μm on mortar properties. Constr. Build. Mater. 20 [9], 615-624. https://doi.org/10.1016/j.conbuildmat.2005.02.025.
).
Comparing the data reported for initial drying with those reported for initial setting time (standardized method for cement), it was found that, during the actual application of the material, the initial drying time is less than the initial setting time. This is associated with the fact that the render of applied material are a few millimeters (2 mm), which allows a faster evaporation of water compared to the experimental procedure of the Vicat needle setting time test. In the case of the final drying time compared to the final setting time, the differences are more evident. During the drying time test, in the external application the proposed mixes took a maximum of 240 minutes to dry, while in the final setting time test, they took more than 24 hours, even 50 hours (mix A4). There is evidently a directly proportional relationship between the initial setting time and the EPS content in the mix, since the higher the EPS content, as in the case of mix A4 (35%), the greater the initial setting time versus mixes A7 and A9 (21%).
4. CONCLUSIONS
⌅-
Different mixes of render mortars with thermal insulation and acoustic absorption properties were produced using different waste materials such as clay brick, masonry mortar and EPS, employed as fine aggregates. The formulations A4, A7 and A9 could be considered suitable for use as interior render mortar type CS-I-W0 classification of the UNE EN-998-1 standard.
-
It was identified that using BW, MW together with EPS in the mixes influences the thermal conductivity compared to the commercial mix AC1. Mix A4 and A9 (classified as type T2 according to UNE EN 998-1), which were found to have low thermal conductivity (0.12 W/m·K and 0.16 W/m·K), those achieved a 79.5% and 71.71% reduction compared to AC1, respectively. The proposed mixes A4, A7, A9 were found to be an Absorbent material for the frequency of 250 Hz, Slightly absorbent for the frequency of 500 Hz, Reflective for the frequency of 1000 Hz, and Highly Absorbent for the frequencies of 2000 Hz and 4000 Hz. Mix A9 can be considered an Extremely absorbent material for the frequency of 4000 Hz.
-
The incorporation of EPS fillers lending the mortars a decrease in their density (1240-1590 kg/m3), further allows a lower consumption of material during application (1.04-1.17 kg/m2/mm) compared to the commercial mix AC1 (2.37 kg/m2/mm), achieving a reduction in consumption of up to 56% for utilization of A4 mortar. A full-scale development of this technological proposal could contribute to mitigating the environmental impacts derived from the high volumes of generation and final disposal of BW, MW and EPS, by allowing their reincorporation into the production cycle as raw material to produce interior render mortars, which constitutes an industrial symbiosis alternative, contributing positively to circular economy processes in the construction sector worldwide.