Journal Information
Download PDF
More article options
Original Article
DOI: 10.1016/j.jmrt.2019.09.038
Open Access
Available online 9 October 2019
Incorporation of mold flux waste in red ceramic
Thaís Queiroz Gomes Vignerona,
Corresponding author
, Carlos Maurício Fontes Vieiraa, Geovana Carla Girondi Delaquaa, Fernando Vernilli Júniorb, Ângelo Cristante Netob
a State University of the North Fluminense – UENF, Advanced Materials Laboratory (LAMAV), Av. Alberto Lamego, 2000, 28013-602 Campos dos Goytacazes, RJ, Brazil
b University of São Paulo – USP, Department of Materials Engineering (DEMAR), Lorena, Brazil
This item has received

Under a Creative Commons license
Article information
Full Text
Download PDF
Figures (15)
Show moreShow less
Tables (3)
Table 1. Elaborated mixtures of mold flux waste and ceramic mass.
Table 2. Chemical analysis of the raw materials (wt.%).
Table 3. Specific surface area of the raw materials.
Show moreShow less

This work has as its objective to evaluate the effect of mold flux waste incorporation in a red ceramic body. The mold flux waste came from an industry of additives for continuous casting of steel, in the municipal area of Guaratinguetá, State of São Paulo, Brazil. Initially, the mold flux waste was characterized in terms of chemical composition, particles size distribution, X-ray diffraction, specific surface area and scanning electron microscopy. Clay mixtures were prepared with additions of 0, 5, 10 and 20wt.% of mold flux waste. Red ceramic specimens were produced by extrusion and then fired in an industrial furnace at 750, 850, 950 and 1050ºC. Some physical and mechanical properties were evaluated. The results indicated that mold flux waste addition optimized the plasticity of the clayey body, increased the flexural and compressive strength and reduced the values for water absorption. The specimens with 5wt.% of mold flux waste, at 1050ºC firing temperature, presented the best results for the properties evaluated, indicating a higher packing for this composition. The incorporation of mold flux waste allowed improvements in the clayey body, producing better quality materials and being an appropriate way of disposal.

Red ceramics
Mold flux
Full Text

Mold flux plays important functions in continuous casting of steel. Basically, this synthetic slag must provide thermal insulation, prevention of steel reoxidation and inclusions absorption when applied on the surface of molten steel. In addition, mold flux lubricates and controls the heat transfer in the gap between the mold of copper and the solidifying steel shell [1–8].

The mold flux is composed by various combinations of raw materials. Frequently used raw materials are quartz, feldspar, fluorite, wollastonite and free carbon [9,10]. The fabrication process of the mold flux implies in the generation of a waste that consists in wet and coarse particles. Those particles cannot be applied in the process of continuous casting once they do not have the recommended granulometry, which is usually 200 mesh. Since the mold flux production occurs in a large scale to attend the continuous casting process, the generation of the mold flux waste occurs in an extensive quantity [11].

It is important to recycle the wastes in different areas such as building materials. The use of wastes as substitutes for clay in the production of red ceramics has been widely studied [12,13]. This environmental correct solutions for the disposal of a large range of solid wastes is possible by the natural variability on the characteristics of clays, the use of simple processing techniques besides relatively low technical performance requisite for the products [14–16].

The incorporation of waste in ceramic makes possible the development of an eco-friendly building material with innumerable advantages like diminish the amount of generated wastes, protect the raw materials from depletion and reduce the environmental pollution. In some cases, the addition of certain residues into a clay matrix enhances the technical performance of the ceramic [17].

The interest in using mold flux waste in red ceramic is mainly due it characteristic that can include biodegradability, combustibility or water solubility [18]. Another concern is the fact that the mold flux waste is usually disposal in industrial landfills. This event promotes negatives environmental impacts that includes a significant source of gases, particulate matter, leachate and very capital intensive [19,20]. The mold flux waste represents an environmental impasse due not only it characteristics but also the costs involved in it correct destination. A huge environment damages can be caused by the inappropriate disposal of this waste, such as the rivers and streams contamination and human health impact by inhalation [21].

This incorporation can improve physical and mechanical properties of ceramic, which can be an economic advantage to the red ceramic [22]. Therefore, this work aimed to incorporate and evaluate the effect of the incorporation of mold flux waste in the physical and mechanical properties of red ceramics.

2Materials and methods2.1Raw materials preparation

A clayey body composed by a mixture of a kaolinite clay, red clay and sand, typically used in the fabrication of bricks and roofing tiles in Campos dos Goytacazes, state of Rio de Janeiro (RJ), Brazil, was incorporated with mold flux waste from the fabrication process of mold flux.

2.2Raw materials characterization

The mold flux and the ceramic mass were initially characterized in terms of their mineralogical, chemical and physical composition as well as firing behavior, by thermo analysis, and morphological aspects. The chemical composition was determined by X-ray fluorescence (XRF) using a PANalytical XRF equipment, model Axios Max. The qualitative mineralogical phase identification were performed by X-ray diffraction (XRD) in powder samples using a PANalytical XRD, model Empyrean, operating with Cu Kα radiation (α=0.15418nm). The particle size distribution were determined by both, sieving and sedimentation methods, according to the norm [23]. The real density of the raw materials was measured by picnometry. Specific surface areas of the raw materials were analyzed using the multi-point BET method. The raw materials microstructure was determined by scanning electronic microscopic (SEM) in a Shimadzu model Superscan SSX500-50. The plasticity of the specimens was evaluated by the Atterberg limits. The liquidity limit was determined in accordance with ABNT NBR 6459 [24], while the plasticity limit determination was performed following to the standard ABNT NBR 7180 [25].

2.3Composition preparation

The elaborated mixtures were made with additions of 0, 5, 10 and 20wt.% of waste in the ceramic mass. Those are shown in Table 1.

Table 1.

Elaborated mixtures of mold flux waste and ceramic mass.

Mixtures  Raw materials (wt.%)
  Ceramic mass  Mold flux waste 
C0MFW  100 
C5MFW  95 
C10MFW  90  10 
C20MFW  80  20 

Rectangular 114mm×25mm×11mm specimens were prepared with the elaborated mixtures. These samples were obtained by extrusion and dried at 110°C. Fig. 1 shows some samples of the developed red ceramic prototype, before firing stage. These samples were fired at 750, 850, 950 and 1050°C in a laboratory furnace. The heating rate was 2°C/min with 3h soaking at the maximum temperature. Cooling occurred by natural convection inside the furnace after it was turned off.

Fig. 1.

Samples of the developed red ceramic prototype, before firing stage (For interpretation of the references to colour in this figure legend, the reader is referred to the web version of this article).

2.4Properties evaluation

After sintering and cooling, the specimens were submitted to water absorption, relative density, linear shrinkage and flexural strength. The water absorption (W.A.) was determined following to ASTM standard procedure [26], according to Eq. (1).

The relative density (R.D.) were measured by dividing the dry bulk density by the real density of the composition, following designation ABNT NBR NM52 [27], according to Eq (2).

The linear shrinkage (L.S.) was obtained by measuring the length of the specimens, using a Mitutoyo caliper with ±0.01mm precision, before and after the firing stage, following to the standard ASTM [28], according to Eq. (3).

The originals specimens were used for flexural test, while to evaluate the compressive strength, a new samples were obtained by cutting the originals specimens with dimensions of 50mm×25mm. In both tests, flexural strength and compressive resistance, the same machine (Instron 5582 universal test machine with 100kN capacity) was utilized. The flexural strength (F.S.) test was carried out following designation ASTM [29] and was realized by loading three points with the load putted by the upper cleat at a speed of 0.5mm/min until the rupture of the specimen. The results was determined according to Eq. (4).

Where P=rupture strength (N); L=Support span (mm); b=Width of test beam (mm); d=height (mm).

The compressive strength (C.S.) was evaluated by using two parallel protection plates, with cross bar moving at 0.1mm/min. Fig. 2 shows some specimens prepared for this test.

Fig. 2.

Specimens prepared for compressive strength test.


The results about compressive strength were determined following to ASTM standard procedure [29], according to Eq. (5).

The sintered specimens microstructure was evaluated by scanning electronic microscopic (SEM) in a Shimadzu model Superscan SSX500-50.

3Results and discussion

Figs. 3 and 4 show the XRD pattern of the raw materials. The major crystalline phases identified in the mold flux waste, Fig. 3, are: quartz(SiO2), wollastonite (CaSiO3) and calcite (CaCO3). Moreover, was identified the presence of albite (NaAlSi3O8), anatase (TiO2) and cryolite (Na3(AlF6)). In Fig. 4, the diffractogram indicates that the major crystalline phases in the clay are: muscovite (KAl2(Si3Al)O10(OH,F)2), quartz (SiO2) and kaolinite (Al2O3.2SiO2.2H2O). Furthermore, was detected the presence of gibbsite minerals (Al(OH)3) and orthoclase (KAlSi3O8).

Fig. 3.

X-ray pattern of the mold flux waste. a: albite; A: anatase; c: calcite; Q: quartz; r: cryolite; w: wollastonite.

Fig. 4.

X-ray pattern of the clay. g: gibbsite; k: kaolinite; m: muscovite; o: orthoclase; Q: quartz.


Table 2 presents the chemical composition and the loss on ignition (LoI) of the raw materials. The mold flux waste is basically composed of high amount of quartz (SiO2) which is associated with the minerals: quartz (SiO2), wollastonite (CaSiO3) and albite (NaAlSi3O8), according to the XRD pattern in Fig. 3. The second major chemical constituent of the mold flux waste is Al2O3 that is probably due to the albite (NaAlSi3O8) and cryolite (Na3(AlF6)) phases. The CaO is mainly due to the calcite (CaCO3) phase. The chemical composition of the clay is based on high amount of SiO2, relative quantity of Al2O3 and low amounts of alkaline oxides. The high percentage of LoI suggests an elevated fraction of clay minerals. The meaningful amount of Fe2O3 in both raw materials gives to the specimens the reddish colour after firing.

Table 2.

Chemical analysis of the raw materials (wt.%).

Raw materials  Oxide compositions
  SiO2  Al2O3  Fe2O3  TiO2  K2MgO  Na2CaO  ZnO  LoIa 
Clay  49,66  23,27  8,98  1,14  0,97  0,29  0,17  0,16  –  15,12 
Mold flux waste  53,08  16,22  5,85  0,61  1,37  1,26  3,01  5,19  1,04  11,75 

Loss on ignition.

Fig. 5 shows the particle size distribution of the clay and mold flux waste. The coarser fraction of the clay, that includes particle size above 20μm, is 45%. The percentage of clay minerals, the one who has particle size below 2μm, is 39%. The clay minerals is responsible for the plasticity of the ceramic mass [30]. The mold flux waste has a high percentage of coarser particle size, when compared to that of the clay. These coarser particles, usually, are associated with quartz. This result corroborates to the raw materials mineralogical analysis, Fig. 3. The real density of the mold flux waste, measured by picnometry, was found to be 2,03g/cm3 while the clay was found to be 2,60g/cm3.

Fig. 5.

Particle-size distribution of the raw materials.


Figs. 6 and 7 represent SEM photomicrographs of the raw materials under study. Fig. 6 shows different aspects of the mold flux waste particle morphology. In this image it is observed different particles’ size and shapes. It exhibits not only fine individual particles but also almost perfect spheres, with different sizes, and particles with irregular format. The solid particles, above 10μm, with a prismatically shape are probably formed by quartz. Fig. 7 presents fine particles agglomerates that is probably formed by the kaolinite clay minerals while coarser particles are quartz [31].

Fig. 6.

SEM photomicrographs of the mold flux waste. (a) 200×; (b) 1000×.

Fig. 7.

SEM photomicrographs of the clay. (a) 200×; (b) 500×.


Table 3 exhibits specific surface area of the raw materials. The clay shows high value of specific surface area, around 31,39m2/g. This result is expected for this type of material, once clays are solids naturally actives exhibiting specific surface areas higher than 1,0m2/g. The mold flux waste shows is excessively smaller value of specific surface area, as compared to the clay, about 4, 51m2/g. The particle size affects deeply the surface area of a solid material [32]. It is important to notice that the sphere is a geometric shape with the smaller surface per volume. This implies that, considering a same mass quantity, the more spherical your particle shape is, Fig. 6, smaller will be your specific surface area.

Table 3.

Specific surface area of the raw materials.

Raw materials  Specific surface area – BET (m2/g) 
Clay  3139 
Mold flux waste  4,51 

An extrusion prognostic using the plasticity of the mixture, is exhibited in Fig. 8. This prognostic is associated mainly to the productivity and workability of the green pieces. It can be noticed that the simple clay ceramic body, C0MFW, is located outside the optimum extrusion region, but is still in an acceptable extrusion region. The result in Fig. 8 shows that the progressive incorporation of mold flux waste has a very significant effect on the extrusion behavior. It is associated to the mold flux waste mineralogical composition that is predominantly composed by quartz, Fig. 3. This mineral acts as a plasticity reducer of the ceramic mass.

Fig. 8.

Extrusion prognostic through Atterberg limits. (●) Locations of the compositions.


With respect to the relative density, it is an important data once only by this analysis is possible to check the mold flux waste effect in the clay compaction behavior [33]. Fig. 9 presents the relative density of the elaborated compositions. One should notice that 10wt.% and 20wt.% tend to decrease the relative density. On the other hand, the 5wt.% addition tend to increase the relative density, as compared to all other compositions. This increase is related to the more efficient particles compaction [34].

Fig. 9.

Relative density of the elaborated compositions.


According to Fig. 10, the linear shrinkage almost does not have significantly variation, for all of compositions in 750°C and 850°C, considering the statistical error. This effect can be related to a low sinterability of the bodies. At 950°C, it can be observed an increase in the linear shrinkage to all composition with addition of mold flux waste, as compared to 0wt.%. This increase becomes more significant at 1050°C. This event is mainly due the vitrification process, which is capable of fill, partially, the open porosity between the particles and provides the shrinkage and densification of the ceramic bodies [35].

Fig. 10.

Linear shrinkage according to the content of mold flux waste incorporated in specimens sintered at 750, 850, 950 and 1050°C.


By contrast, Fig. 11 shows that the mold flux waste addition decreases the water absorption with the temperature increment. This decrease is more significant for 5wt.% addition. This result can be related to the more efficient compaction behavior in this specimen, Fig. 9. The increase in linear shrinkage and the decrease in water absorption with mold flux waste addition are consequences of the higher fluxes content, Table 2, as compared to that of the clay. At higher temperatures the fluxes (K2O and Na2O) cause an increase in the liquid phase promoting densification and improving the sintering process.

Fig. 11.

Water absorption according to the content of mold flux waste incorporated in specimens sintered at 750, 850, 950 and 1050°C.


Figs. 12 and 13 show the results of flexural rupture strength and compressive strength, respectively. The flexural strength is a property tightly dependent on the porosity and microstructural defects of the bodies. One should observe that the mold flux waste addition increases the flexural strength with the temperature increment, specially at 1050°C. It is already expected, due the densification. It is relevant to notice that the addition of 5wt.% get the higher values of flexural strength for all temperatures analyzed, Fig. 12. A reduction in flexural strength is observed with the 10 and 20wt.% addition of mold flux waste, when compared to 5wt.%. One should wonder why the improved densification obtained by the flux action of the mold flux waste does not result into a better flexural strength for all compositions. Even though the mold flux waste incorporation contributes to diminish the open porosity, the median pore diameter increases sharply. This event, together with the higher amount of quartz in the 10 and 20wt.% compositions, may introduce large enough pores and micro-craks to implicate in a drop of the flexural strength [36].

Fig. 12.

Flexural strength according to the content of mold flux waste incorporated in specimens sintered at 750, 850, 950 and 1050°C.

Fig. 13.

Compressive strength according to the content of mold flux waste incorporated in specimens sintered at 750, 850, 950 and 1050°C.


The compressive strength, similar as flexural strength, presented higher values for specimens with mold flux waste addition, which reaches 27% at 1050°C, when comparing the compositions containing 20 and 0wt.% of waste. The increase in temperatures, in consortium with the incorporation of mold flux waste, contributed positively to the mechanical resistance.

Scanning electron micrographs of the fracture surface of bodies without addition, C0MFW, and with 20wt.% of mold flux waste, C20MFW, fired at 750°C and 1050°C, are shown in Figs. 14 and 15, respectively. It can be notice that both bodies present a rough fracture surface. The micrographs of C0MFW show a comparatively larger quantity of defects such as cracks and voids. On the other hand, C20MFW shows a better-sintered microstructure with smoother areas e fewer defects as compared to C0MFW, specially at 1050°C which the higher temperature makes possible a more efficient vitrification process, Fig. 15. This may be due to the flux action of the mold flux waste, that improves the sintering process.

Fig. 14.

SEM photomicrographs of fractured region of the compositions (a) C0MFW and (b) C20MFW fired at 750°C – 500×.

Fig. 15.

SEM photomicrographs of fractured region of the compositions (a) C0MFW and (b) C20MFW fired at 1050°C – 1000×.


In this work, the characterization and evaluation of the effect of a industrial waste, mold flux waste, generated during the production of mold flux into red ceramic led to the following conclusions:

  • The mold flux waste can improve the extrusion process, optimizing the plasticity.

  • The mold flux waste incorporation decreases the open porosity of the fired clay. Consequently, the water absorption decreased with the mold flux waste content and, by contrast, the flexural strength and compressive strength increased.

  • The use of mold flux waste is viable for some types of ceramic pavers. The results of water absorption and compressive strength indicated that the specimens with 5wt.% of mold flux waste, with a firing temperature of 1050°C, can be produced for implementation systems hard (type R) and implementation systems flexible (type F) according to ASTM [37]. Furthermore, this same composition at 1050°C, can be produced for floors where the pavers may be frozen while saturated with water (SX) according to ASTM [38].

  • The SEM microstructural analysis showed that the composition with 20wt.% of mold flux waste has a finer fracture surface with less defects as compared to the clay without mold flux waste incorporation.

  • The use of mold flux waste in red ceramic can be a technological solution to the problems caused by the indiscriminate disposal into the environment.

Conflicts of interest

The authors declare no conflicts of interest.


The authors thank the support provided by the Brazilian agencies: CAPES, CNPq and FAPERJ.

K.C. Mills.
A short history of mould powders.
Ironmak Steelmak, 44 (2017), pp. 326-332
Z. Cai, B. Song, L. Li, Z. Liu.
Effects of CeO2 on melting temperature, viscosity and structure of mold fluxes for casting rare earths alloyed steels.
10th international symposium on high-temperature metallurgical processing, Springer, (2019), pp. 381
M. Görnerup, M. Hayashi, C.Å Däcker, S. Seetharaman.
Mould fluxes in continuous casting of steel–characterization and performance tuning.
The South African Institute of Mining and Metallurgy. Proc. 7th Int. Conf. on Molten Slags, Fluxes and Salts, pp. 745-752
J.J.A. Souza, J.C. Pontes Junior, S.S. Souza, M.C.C. Bezerra, C.A.G. Valadares, D.A. Almeida.
Analysis of influence of fluorine-free mould flux to continuous casting of slabs of low carbon steel.
43Rd Steelmaking Seminar–International, (2012),
A.A. Diego, L. Demuner, G.R.T. Santos, K.T. Matos, M.C.C. Bezerra, C.A.G. Valadares, et al.
The impact of chemical composition change of mold flux applied in low carbon steel in the wear of SEN.
METEC and 2nd European Steel Technology and Application Days Conference,
R. Saraswat, A.B. Fox, K.C. Mills, P.D. Lee, B. Deo.
The factors affecting powder consumption of mould fluxes.
Scand J Metall, 33 (2004), pp. 85-91
K.C. Mills.
Structure and properties of slags used in the continuous casting of steel: part 1 conventional mould powders.
Isij Int, 56 (2016), pp. 1-13
K.C. Mills, A.B. Fox.
The role of mould fluxes in continuous casting-so simple yet so complex.
Isij Int, 43 (2003), pp. 1479-1486
Y.G. Maldonado, A.E. Castillejos.
A new method for estimating the isothermal devitrification and crystallization of mold powder slags from non-isothermal DSC data.
Mater Des, 83 (2015), pp. 728-735
J.A. Kromhout.
Mould powders for high speed continuous casting of steel. [D.SC. thesis].
Technische Universiteit Delft, (2011),
K.C. Mills.
How mold fluxes work.
Treatise on process metallurgy. Volume 3: industrial processes, pp. 435-475
A. Al-Fakih, B.S. Mohammed, M.S. Liew, E. Nikbakht.
Incorporation of waste materials in the manufacture of masonry bricks: an update review.
J Build Eng, 21 (2019), pp. 37-54
E. Esmeray, M. Atıs.
Utilization of sewage sludge, oven slag and fly ash in clay brick Production.
Constr Build Mater, 194 (2019), pp. 110-121
P.H.S. Almeida, J.D.M. Franco, C.R.G. Tavares.
Influence of clay type in the solidification stabilization process of textile sludge.
Cerâmica, 61 (2015), pp. 137-144
Y.L. Oliveira, J.Z. Linhares, L. Ancelmo, R.A.L. Soares.
Study of reuse of ceramic tile waste (Chamote) in bulk formulation for ceramic blocks.
Cerã¢mica Ind, 21 (2016), pp. 45-50
L. Wiemes, U. Pawlowsky, V. Mymrin.
Incorporation of industrial wastes as raw materials in brick’s formulation.
J Clean Prod, 142 (2017), pp. 69-77
O. Kizinievič, V. Kizinievič, I. Pundiene, D. Molotokas.
Eco-friendly fired clay brick manufactured with agricultural solid waste.
Arch Civ Mech Eng, 18 (2018), pp. 1156-1165
Brazilian Association of Technical Standards – ABNT, solid waste – classification, NBR 10004, Rio de janeiro (2004) Brazil.
G. Sujetovienė, P. Smilgaitis, R. Dagiliūtė, J. Žaltauskaitė.
Metal accumulation and physiological response of the lichens transplanted near a landfill in central Lithuania.
Waste Manag, 85 (2019), pp. 60-65
F. Owusu-Nimo, S. Oduro-Kwarteng, H. Essandoh, F. Wayo, M. Shamudeen.
Characteristics and management of landfill solid waste in Kumasi, Ghana.
Sci Afr, (2019),
L.F. Amaral, Carvalho JPRG, B.M. Silva, G.C.G. Delaqua, S.N. Monteiro, C.M.F. Vieira.
Development of ceramic paver with ornamental rock waste.
J Mater Res Technol, 8 (2019), pp. 599-608
T.G. Cota, E.L. Reis, R.M.F. Lima, R.A.S. Cipriano.
Incorporation of waste from ferromanganese alloy manufacture and soapstone powder in red ceramic production.
Appl Clay Sci, 161 (2018), pp. 274-281
Brazilian Association of Technical Standards – ABNT, soil- particle size analysis, NBR –7181, Rio de janeiro (1984) Brazil.
Brazilian Association of Technical Standards ABNT, Determination of the Liquidity Limit, NBR – 6459, Rio de Janeiro. (1984) Brazil.
Brazilian Association of Technical Standards – ABNT, Determination of the Plasticity Limit, NBR – 7180, Rio de Janeiro (1984) Brazil.
ASTM – American Society for Testing and Materials.
Water absorption, bulk density, apparent porosity, and apparent specific gravity of fired whiteware products C373.
Brazilian Association of Technical Standards – ABNT, Determination of specific mass and apparent specific mass, NBR – NM52, Rio de Janeiro (2003) Brazil.
ASTM – American Society for Testing and Materials.
Drying and firing shrinkages of ceramic whiteware clays C326.
ASTM – American Society for Testing and Materials.
Flexural properties of ceramic whiteware materials C674.
P.S. Santos.
2nd ed., Edgard Blucher, (1989), pp. 408
D.C.N.S.P. Reis.
The importance of studying the specific surface area and porosity of magnesium stearate for the pharmaceutical sector. [M.SC. dissertation].
Rio de Janeiro: FIOCRUZ, (2013),
R.P. Mulazzani, P.I. Gubiani.
Model of soil surface area estimation using the particle size curve.
Sociedade Brasileira de Ciência do Solo, (2016),
A.S.C. Morais.
Glass waste incorporation of red ceramic fluorescent lamp. [D.SC. thesis].
State University of the North Fluminense Darcy Ribeiro, (2013),
M.P. Babisk, F.W.H. Vidal, W.S. Ribeiro, M.C. Aguiar, M.C.B. Gadioli, C.M.F. Vieira.
Incorporation of quartzite waste in red ceramic.
HOLOS, 28 (2012), pp. 169
L. Queiroz, S. Monteiro, C. Vieira.
Effect of sand utilization on red ceramic processing and properties.
Cerâmica, 56 (2010), pp. 279-284
M. Dal Bó, V. Cantavella, E. Sanchéz, F.A. Gilabert, A.O. Boschi, D. Hotza.
An estimate of quartz content and particle size in porcelain tiles from young’s modulus measurements.
Ceram Int, 43 (2017), pp. 2233-2238
ASTM – American Society for Testing and Materials.
Standard specification for heavy vehicular paving brick, C1272.
ASTM – American Society for Testing and Materials.
Standard specification for pedestrian and light traffic paving brick, C902.
Copyright © 2019. The Authors
Journal of Materials Research and Technology

Subscribe to our newsletter

Article options
Cookies policy
To improve our services and products, we use cookies (own or third parties authorized) to show advertising related to client preferences through the analyses of navigation customer behavior. Continuing navigation will be considered as acceptance of this use. You can change the settings or obtain more information by clicking here.