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Article

Coconut-Fiber Composite Concrete: Assessment of Mechanical Performance and Environmental Benefits

by
Emilio Vélez
1,
Ricardo Rodríguez
1,
Nicolay Bernardo Yanchapanta Gómez
1,*,
Edgar David Mora
1,
Luis Hernández
1,
Jorge Albuja-Sánchez
2,3 and
María Inés Calvo
2
1
Departamento de Ingeniería Civil y Ambiental, Escuela Politécnica Nacional (EPN), Quito 170143, Ecuador
2
Department of Civil Engineering, Laboratory of Materials Resistance, Soil Mechanics, Pavements and Geotechnics, Pontificia Universidad Católica del Ecuador (PUCE), Quito 170143, Ecuador
3
Department of Engineering, University of Ferrara, 44121 Ferrara, Italy
*
Author to whom correspondence should be addressed.
Fibers 2022, 10(11), 96; https://doi.org/10.3390/fib10110096
Submission received: 12 July 2022 / Revised: 5 September 2022 / Accepted: 28 September 2022 / Published: 9 November 2022
(This article belongs to the Special Issue Natural Fiber Competitiveness and Sustainability)

Abstract

:
The purpose of this qualification work is to study the physical and mechanical behavior of concrete with the addition of 0.5% and 1% coconut fiber, which has been subjected to two chemical treatments to reduce its degradation. The coconut fibers were extracted from the raw material and cut into pieces 4 cm long. Subsequently, the fibers were subjected to two chemical treatments. The first involved immersing the fibers in 4% sodium hydroxide (NaOH) solution, and the second treatment involved coating them with gum arabic and silica fume. A total of 50 samples of fibers were collected in their natural and post-treated state to be tested. The dosage was prepared for design strengths of 210 and 240 kg/cm2 (20.59 and 23.54 MPa), so that the percentages of 0.5% and 1% volume of coconut fiber, for the two treatments selected, replaced the respective volume of coarse aggregates. The cylinders with 1% addition of fibers had the best performance for the design strength of 20.59 MPa, including the cylinders without fibers. Those with 0.5% addition of fibers presented better performance for the 23.54 MPa dosage, although this was lower than the cylinders without fibers. In all cases, the cylinders with NaOH-treated fibers outperformed their counterparts with fibers treated with gum arabic and silica fume. Finally, a CO2 balance was determined, and an environmental gain up to 14 kg in CO2 emissions was established for each cubic meter of composite concrete.

Graphical Abstract

1. Introduction

Concrete is a dominantly used construction material worldwide. Its manufacture involves the release of quantities of greenhouse-gas emissions to the atmosphere each year, accounting for 5% of global anthropogenic CO2 emissions [1]. Growing environmental awareness has led to several efforts to reduce concrete greenhouse emissions, without undermining its physical and mechanical properties. Different strategies, such as the addition of fly ash and furnace slags [1,2] and the inclusion of recycled PET fiber [3] or recycled concrete aggregates and agriculture and industry by-products [4,5], have been applied. Research on the usage of natural fibers, owing to their economy, low energy consumption, and wide availability [6,7,8] has also been conducted.
As a by-product of the coconut industry, coconut husk fiber is used in concrete manufacturing, representing a possibility of obtaining a composite material with improved mechanical characteristics and low cost [9]. An additional, less evident benefit is the CO2 sequestration achieved by encapsulating the fibers in the mixture because the final disposal method of coconut husk, owing to various circumstances, is usually incineration [10,11].
Despite the economic and environmental advantages listed above, the organic nature of coir fibers renders them vulnerable to degradation, owing to the environmental conditions in which the composite material is found and to the chemical aggressiveness of the cementitious matrix [12,13]. For this reason, mitigation measures, including different chemical treatments, are necessary to use. Fiber-matrix adhesion also plays an important role in composite concrete performance [12]. Some of these treatments are of the hydrophobic type, i.e., their purpose is to reduce the hydrophilic behavior of the fibers and improve fiber-matrix adhesion [14]. Hydrophobic treatments include acetylation and mercerization, as well as the use of sodium chloride, methacrylate, isocyanate, and silane, among others [14]. An alternative approach is to protect the fiber by adding silica fume, thereby producing a local pozzolanic effect (in the vicinity of the fiber) that increases the protection against chlorides [15].
The length of the fiber included in the concrete mix is a variable of significant influence on the mechanical performance of the final product. Previous studies have shown that specimens with better characteristics are obtained with lengths close to 5 cm, compared with 2.5 and 7.5 cm [16].
The present study sought to identify important differences in the physical and mechanical characteristics between composite concrete cylinders with coir fibers cut to 4 cm long. The latter was subjected to two different treatments (mercerization and silica fume coating) to make the fibers more endurable to degradation and adherent to the cementitious matrix, both highly desirable qualities in fibers [12]. The goal of this research was to include chemical treatment as an additional influential variable in coconut-fiber composite concrete performance. We also explored how these chemical treatments influenced the strength of the fibers alone. We further estimated the environmental benefit of using coconut fibers in concrete, estimating the potential amount of carbon dioxide produced by burning coconut husk or fiber, accounting for in-concrete fiber and husk remainders (pith) from fiber extraction. These remainders, if not incinerated, would be returned to land, thereby further decreasing CO2 emissions.
This paper is organized as follows. Section 2 presents the materials and methods; Section 3 presents the results and discussion. Finally, the conclusions are reported in Section 4.

2. Materials and Methods

2.1. Materials

Coconut husk was purchased from farmers in the town of Cojimíes, Ecuador. Aggregates and cement were purchased from Holcim, Ecuador. Caustic soda and gum arabic were purchased from La Casa del Químico S.A. Silica fume (SikaFumeTM) was purchased from Aplika S.A.
The cement and coarse and fine aggregates were subjected to several essays to examine their properties and used later to determine the mix design. Table 1 shows the values for coarse and fine aggregates, extracted and processed from andesites in Pifo, Ecuador.
In the case of cement, Holcim FuerteTM type I was used. Its properties are shown in Table 2.
The husk was progressively soaked and cleaned so that the fibers could be separated from the pith. Once the fiber was sufficiently clean, its properties were found in a similar way to the aggregates, as shown in Table 3. These properties were used to determine the fiber amounts in each mix and the fiber dry mass for CO2-footprint estimations.
Subsequently, the fiber was cut into pieces 40 mm long according to the criteria of [16,24]. A portion of the staple fibers was immersed in a 4% by weight solution of sodium hydroxide (NaOH) for 24 h [25]. Afterwards, the fibers were rinsed in tap water until a neutral pH was reached and allowed to drain for storage. The other part of the fibers was dipped in liquid gum arabic for 1 min to generate bonding, followed by the adhesion of silica fume around them [26]. The fibers were left to dry in the shade for later storage. Figure 1 shows the appearance of the fibers during the different chemical treatments.
A sample of uncut fibers was collected and subjected to the treatments described above. Another part was left untreated (50 specimens by typology). These were labeled, and their weight and length were taken. They were tested at the Polytechnic Textile Center from the National Polytechnic School (EPN). An Instron 3345 tensile testing equipment was used, following the guidelines of the ASTM D2256 standard [27]. The specimens were located in the apparatus and tensile loads at a crosshead speed of 30 mm/minute were applied until break. Breaking force (N) and elongation (mm/mm) were measured using the machine, obtaining the toughness (N/tex) as a result of dividing the breaking force over linear density (tex), and the latter was calculated with the specimen’s weight and length.

2.2. Specimen Preparation and Testing

The specimens were prepared and tested at the Laboratory of Materials Strength, Soil Mechanics, Pavements, and Geotechnics of the Pontifical Catholic University of Ecuador. Cylinders 30 cm in height and 15 cm in diameter were prepared. Cylinders with and without fibers were manufactured for design strengths of 20.59 and 23.54 MPa at ages 14, 28, and 56 days. The cylinders to which fiber was added were distinguished by the volume percentage of fiber (0.5% and 1%) and by the treatment to which the fiber was subjected (mercerization or silica-fume treatment). The design mixes were elaborated starting from the ACI 211.1 standard [28], and then changes were introduced to reach the design strengths. The final mix designs are detailed in Table 4.
Seven cylinders were manufactured for each category (mix design, cylinder age, fiber content, and fiber treatment), giving a total of 210 cylinders.
At their corresponding ages, the cylinders were subjected to the compression test following the procedure dictated in the ASTM C39 standard [29]. Additionally, for the 56-day cured cylinders, the modulus of elasticity was determined in accordance with ASTM C469 [30]. An example of the specimens during the respective tests is shown in Figure 2.

2.3. Determination of Compressive Strength and Modulus of Elasticity

With the maximum strength results obtained from the compression tests of the cylinders, the maximum compressive stress or f’c (MPa) was obtained by dividing the maximum load resisted by the cylinder over its cross-sectional area.
Two out of seven fifty-five-day cylinders were selected for the modulus of elasticity test. The data used were provided by a compressometer, which recorded the applied loads and deformations as the test was performed. Each one of these values enabled the calculation of stress S (MPa) by dividing the maximum load resisted by the cylinder over its cross-sectional area. The unit strain ε was computed by dividing the length variation taken from the compressometer over the average length of the cylinder. S and ε were used to obtain the modulus of elasticity according to ASTM C469 standards [30].

2.4. Carbon-Footprint Determination

To determine the carbon footprint, we started by accounting for the organic components of the husk (i.e., fiber and pith) and dry fiber, as obtained from [31,32]. The carbon percentage of each one of them was determined according to the work of Vilela [10] and Encinas Soto [33]. With the above information, a weighted sum of the carbon contributions by component was made. Accordingly, we were finally able to establish the CO2 equivalent. The details are shown in Table 5.
Once the percentage of carbon was obtained, the mass of CO2 was determined by mass balance, which was similar to Vilela’s method [10], as indicated in Equation (1).
M CO 2 ( kg ) = M CO 2 M C m C
where M CO 2 is the molecular mass of CO2, equal to 44.01 g/mol, M C is the molecular mass of carbon, equal to 12.01 g/mol, and m C is the mass of carbon per unit of matter (fiber and husk, dimensionless).
Laboratory calculations (based on Table 3 data) yielded a dry bulk density of 237.04 kg/m3 of coconut fiber (including possible voids). Thus, having the proposed percentages in the volumes of 0.5% and 1% of coconut fiber enabled us to determine the dry mass of fiber of 1.18 and 2.37 kg per m3 of the concrete mix, respectively.
Considering the research of Puentes and Joya [31], who found that the dry weight of the coconut fiber represents about 30% of the husk as a whole, we estimated that producing the above-mentioned amounts of dry coconut fiber required the use of 3.95 and 7.90 kg of coconut husk. Thus, the CO2 emissions saved (directly or indirectly) can be found using Equation (2).
E CO 2 ( kg ) = Pm CO 2
where P is the dry mass of matter (kg) and m CO 2 is the mass of CO2 per unit of matter (fiber or husk, dimensionless).

3. Results and Discussion

3.1. Physical and Mechanical Characteristics of the Fiber

The fibers were divided into the following three typologies: NT (untreated fibers), CS (fibers treated with caustic soda or NaOH), and SF (fibers treated with silica fume). The results are illustrated in Figure 3. The NaOH or caustic soda treatment promoted a slight increase in the maximum elongation of the fibers compared with the NT and SF fibers. Likewise, a higher linear density was found in relation to the other typologies. However, a lower value of average breaking strength (and consequently, of toughness) was obtained for the CS fibers in relation to the NT and SF fibers. The high dispersion of the observed values was primarily due to the heterogeneity of coir fibers, which can present imperfections and defects in significant quantities [34].
In general, the mechanical properties of coconut fiber were lower than those of other natural and synthetic fibers, which could mean less load transfer from the composite to fiber, and thus lower composite strength [35]. Nonetheless, the decrease in CS and SF properties could be balanced with better fiber-matrix adhesion, meaning better composite properties [35].

3.2. Composite Concrete Density

We found that adding fibers at the proposed percentages had little effect on the density of the composite concrete, finding values between 2265 and 2298 kg/m3 in the case of the design strength of 20.59 MPa and between 2260 and 2274 kg/m3 in the case of the design strength of 23.54 MPa. This result agreed with that of Ismail [36], who found that the effect of fiber addition on the density had little significance in low fiber–cement ratios.

3.3. Compressive Strength

Table 6 shows the compressive strengths obtained for the different types of cylinders for design strengths of 20.59 MPa, i.e., NF (without fiber), CS (fibers with caustic soda treatment), and SF (fibers with silica-fume treatment), at fiber contents of 0.5% and 1% and ages of 14, 28, and 56 days.
Figure 4 shows the effect of the fibers with their respective treatments on the compressive strength of the cylinders for the base dosage of 20.59 MPa. In this case, the cylinders with fibers generally presented higher compressive strengths than those without fibers. Particularly, better results were generally obtained with the cylinders that contained CS fiber in their composition.
Moreover, except for the case of SF 1% at 14 days, the strengths of the SF cylinders were lower than that of the CS cylinders. In the case of CS cylinders, the results can be compared with those of Yan et al. [37], who used a design strength at the age of 28 days of 20 MPa, fiber length of 50 mm, and an amount of fibers equal to 1% by mass of cement. As in the present research, better results are obtained in the composite concrete with NaOH-treated fibers than in the concrete without fibers.
Table 7 shows the compressive strengths obtained for the different types of cylinders for design strengths of 23.54 MPa as aforementioned, and for the ages of 14, 28, and 56 days.
Figure 5 shows the effect of fibers with their respective treatments on the strength of the cylinders. In this case, CS and SF cylinders had lower compressive strengths than those without fibers. For high design strengths, coir fibers tended to produce a reduction in the compressive strength of the composite concrete, as demonstrated by Ogunbode et al. [38] SF cylinders, for the ages of 14 and 28 days, exceeded the CS cylinders’ compressive strength by 0.5% in volume fiber content and by 1% fiber content and 56 days’ age (0.5% and 1% volume fiber content).

3.4. Modulus of Elasticity

Figure 6 shows the results of the modulus of elasticity for the different types of cylinders prepared for the design strength of 20.59 MPa. Cylinders with fibers had a lower modulus of elasticity than those without fibers (related to a slight reduction in stiffness and inferior toughness), similar to what Ali [39] obtained for the same fiber content and length. Cylinders with 1% fiber also had higher modulus of elasticity values than those with 0.5%. Among the two types with fiber, CS cylinders had a higher modulus of elasticity than SF cylinders.
Figure 7 shows the results of the modulus of elasticity for the different types of cylinders produced and for a design strength of 23.54 MPa. Once again, the values of modulus of elasticity were higher in the case of cylinders without fibers or NF, and among the cylinders with fibers, the highest values were provided by CS cylinders. In this case, the values were slightly higher with a volume fraction of fibers of 0.5%, in relation to the volume fraction of 1%.

3.5. CO2-Emission Savings

Figure 8 shows an estimate of the emissions saved by encapsulating the carbon contained in the fibers. In the case of direct CO2 emissions savings, this value amounts to 4.55 kg CO2 emissions for concrete with 1% fiber. However, if the emissions saved by the other husk components that were needed to obtain the fiber from the mix were considered, and after processing the fiber were also used for other purposes, it accounted for 14.49 kg CO2 emissions. Flower and Sanjayan [1] estimated that a typical 25 MPa concrete production releases 290 kg CO2 per m3. With 1% fiber replacement, it would enable a CO2 emission reduction of around 5%, which increases with decreased design strength, owing to less cement inclusion (the most polluting concrete component) [1].

4. Conclusions

Experiments with coconut-fiber composite concrete were performed by changing the fiber treatment, fiber volume proportion, mix design, and cylinder ages. The maximum values of the studied properties can be observed in a combination of NaOH-treated fibers, with lower design strength, and lower fiber volume proportion. Fiber-matrix adhesion played a key role in improving the performance of CS cylinders compared with SF cylinders. Fiber inclusion in concrete mixes was a feasible strategy to reduce greenhouse-gas emissions during concrete manufacturing, owing to the acceptable mechanical properties and complementarity to the corresponding strategies reviewed in the literature. Based on our results, the following conclusions were drawn:
  • The best results were obtained for concrete cylinders made with a design strength of 20.59 MPa, including a 0.5% volume fraction of NaOH-treated fibers, which slightly exceeded that of fiber-free concrete. Mostly, increasing the fiber volume fraction and design compressive strength led to a major disadvantage in compressive strength and modulus of elasticity of composite concrete, compared with fiber-free concrete.
  • Concrete density was not significantly affected by the volume fractions used in this research. More coconut fiber would be needed in the concrete mix to achieve lower densities.
  • The mechanic properties of the fibers were similar among the CS and SF fibers. We observed a reduction in their features compared with the NT fibers, except for elongation and linear density, for which CS fibers achieved better performance.
  • In all cases, the dosages of composite concrete with fibers exceeded the expected compressive strengths of 20.59 and 23.54 MPa, demonstrating the feasibility of adding 0.5% and 1% fibers and maintaining admissible mechanical properties.
  • Emission savings of up to 4.54 kg CO2 were observed, considering only the contribution of the fibers and up to 14.49 kg CO2 per cubic meter of concrete, considering the non-incineration of all components of the original husk, with the addition of 1% of fibers.

Author Contributions

Conceptualization, R.R., E.V. and E.D.M.; methodology, E.V.; software, E.V.; validation, R.R., E.V. and N.B.Y.G.; formal analysis, N.B.Y.G.; investigation, R.R. and E.V.; resources, N.B.Y.G., R.R. and E.V.; data curation, N.B.Y.G.; writing—original draft preparation, R.R. and E.V.; writing—review and editing, R.R. and E.V.; visualization, E.V.; supervision, L.H.; project administration, L.H.; funding acquisition, N.B.Y.G., J.A.-S. and M.I.C. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

The authors acknowledge Hilda Trujillo of the Department of Chemical Engineering—Polytechnic Textile Center, National Polytechnic School (EPN) for her support in fiber testing.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. (a) Appearance of fibers during NaOH treatment, and (b) silica-fume treatment.
Figure 1. (a) Appearance of fibers during NaOH treatment, and (b) silica-fume treatment.
Fibers 10 00096 g001
Figure 2. (a) Specimen for compression test, and (b) modulof elasticity test.
Figure 2. (a) Specimen for compression test, and (b) modulof elasticity test.
Fibers 10 00096 g002
Figure 3. (a) Average breaking strength, (b) linear density, (c) toughness, and (d) elongation.
Figure 3. (a) Average breaking strength, (b) linear density, (c) toughness, and (d) elongation.
Fibers 10 00096 g003
Figure 4. Effect of fiber percentage on compressive strength (base dosage of 20.59 MPa).
Figure 4. Effect of fiber percentage on compressive strength (base dosage of 20.59 MPa).
Fibers 10 00096 g004
Figure 5. Effect of fiber percentage on compressive strength (base dosage of 23.54 MPa).
Figure 5. Effect of fiber percentage on compressive strength (base dosage of 23.54 MPa).
Fibers 10 00096 g005
Figure 6. Modulus of elasticity for design strength of 20.59 MPa.
Figure 6. Modulus of elasticity for design strength of 20.59 MPa.
Fibers 10 00096 g006
Figure 7. Modulus of elasticity for design strength of 23.54 MPa.
Figure 7. Modulus of elasticity for design strength of 23.54 MPa.
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Figure 8. Direct and indirect CO2 emissions saved per cubic meter of concrete.
Figure 8. Direct and indirect CO2 emissions saved per cubic meter of concrete.
Fibers 10 00096 g008
Table 1. Properties of coarse and fine aggregates.
Table 1. Properties of coarse and fine aggregates.
Ref.PropertyUnitCoarse
Aggregate
Fine
Aggregate
[17]Nominal maximum sizemm19.05-
[17]Fineness modulus--2.76
[18,19]Density (oven dried)g/cm31.892.19
[18,19]Density (saturated surface dry)g/cm32.352.23
[18,19]Absorption%2.002.07
[20]Dry compacted densityg/cm31.49-
[21]Moisture content%2.722.66
Table 2. Properties of concrete.
Table 2. Properties of concrete.
Ref.PropertyUnitValue
[22]Densityg/cm32.68
[23]Normal consistency (moisture)%23
Table 3. Properties of coconut fiber.
Table 3. Properties of coconut fiber.
PropertyUnitValue
Density (saturated surface dry)g/cm30.582
Absorption%145.5
Table 4. Mix designs.
Table 4. Mix designs.
CodeDesign f’c
(MPa)
CementFine
Aggregate/
Cement
Coarse
Aggregate/
Cement
Water/
Cement
M120.5912.071.660.57
M223.5411.771.360.50
Table 5. Percentage of carbon in dry husk and fiber (discounting moisture).
Table 5. Percentage of carbon in dry husk and fiber (discounting moisture).
ComponentC
(%)
Mass in Husk (%)C Husk
(%)
Mass in
Fiber (%)
C Fiber
(%)
Pectin37.1119.267.153.171.17
Cellulose44.4428.4712.6545.8520.37
Hemi-cellulose45.1711.495.190.260.12
Lignin63.439.525.0448.3830.67
Total 50.03 52.34
Table 6. Compressive strength results for base dosage of 20.59 MPa.
Table 6. Compressive strength results for base dosage of 20.59 MPa.
Mixture14 Days28 Days56 Days
NF20.01 (0.69)23.26 (1.64)26.91 (2.71)
CS 0.5%20.09 (0.99)26.58 (0.96)34.15 (1.65)
CS 1%21.19 (1.19)26.38 (0.42)29.79 (1.68)
SF 0.5%18.49 (0.62)24.75 (1.60)24.60 (1.43)
SF 1%24.16 (1.35)24.19 (1.27)28.42 (1.85)
Table 7. Compressive strength results for base dosage of 23.54 MPa.
Table 7. Compressive strength results for base dosage of 23.54 MPa.
Mixture14 Days28 Days56 Days
NF26.75 (0.64)30.97 (1.52)36.69 (1.84)
CS 0.5%21.05 (2.98)28.52 (3.12)36.15 (1.81)
CS 1%22.32 (1.06)30.32 (1.11)34.36 (2.30)
SF 0.5%24.11 (0.96)30.82 (0.95)31.29 (3.49)
SF 1%20.82 (1.31)26.01 (1.38)32.75 (2.24)
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MDPI and ACS Style

Vélez, E.; Rodríguez, R.; Yanchapanta Gómez, N.B.; Mora, E.D.; Hernández, L.; Albuja-Sánchez, J.; Calvo, M.I. Coconut-Fiber Composite Concrete: Assessment of Mechanical Performance and Environmental Benefits. Fibers 2022, 10, 96. https://doi.org/10.3390/fib10110096

AMA Style

Vélez E, Rodríguez R, Yanchapanta Gómez NB, Mora ED, Hernández L, Albuja-Sánchez J, Calvo MI. Coconut-Fiber Composite Concrete: Assessment of Mechanical Performance and Environmental Benefits. Fibers. 2022; 10(11):96. https://doi.org/10.3390/fib10110096

Chicago/Turabian Style

Vélez, Emilio, Ricardo Rodríguez, Nicolay Bernardo Yanchapanta Gómez, Edgar David Mora, Luis Hernández, Jorge Albuja-Sánchez, and María Inés Calvo. 2022. "Coconut-Fiber Composite Concrete: Assessment of Mechanical Performance and Environmental Benefits" Fibers 10, no. 11: 96. https://doi.org/10.3390/fib10110096

APA Style

Vélez, E., Rodríguez, R., Yanchapanta Gómez, N. B., Mora, E. D., Hernández, L., Albuja-Sánchez, J., & Calvo, M. I. (2022). Coconut-Fiber Composite Concrete: Assessment of Mechanical Performance and Environmental Benefits. Fibers, 10(11), 96. https://doi.org/10.3390/fib10110096

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