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materials
Article
Technical and Environmental Viability of a Road Bicycle Pedal
Part Made of a Fully Bio-Based Composite Material
David Hernández-Díaz 1, * , Ricardo Villar-Ribera 2,*, Ferran Serra-Parareda 3, Rafael Weyler-Pérez 4,
Montserrat Sánchez-Romero 4, JoséIgnacio Rojas-Sola 5and Fernando Julián6
Citation: Hernández-Díaz, D.;
Villar-Ribera, R.; Serra-Parareda, F.;
Weyler-Pérez, R.; Sánchez-Romero,
M.; Rojas-Sola, J.I.; Julián, F. Technical
and Environmental Viability of a
Road Bicycle Pedal Part Made of a
Fully Bio-Based Composite Material.
Materials 2021,14, 1399. https://
doi.org/10.3390/ma14061399
Academic Editor: J ¯
anis Andersons
Received: 19 February 2021
Accepted: 10 March 2021
Published: 13 March 2021
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1Serra Húnter Programme, Department of Engineering Graphics and Design, Polytechnic University of
Catalonia, 08222 Terrassa, Spain
2Department of Engineering Graphics and Design, Campus Manresa, Polytechnic University of Catalonia,
08242 Manresa, Spain
3LEPAMAP Research Group, University of Girona, 17003 Girona, Spain; ferran.serrap@udg.edu
4Department of Strenght Materials and Structural Engineering, Polytechnic University of Catalonia,
08222 Terrassa, Spain; rafael.weyler@upc.edu (R.W.-P.); montserrat.sanchez@upc.edu (M.S.-R.)
5Department of Engineering Graphics, Design and Projects, University of Jaén, 23071 Jaén, Spain;
jirojas@ujaen.es
6
Design, Development and Product Innovation, Department of Organization, Business, University of Girona,
17003 Girona, Spain; fernando.julian@udg.edu
*Correspondence: david.hernandez-diaz@upc.edu (D.H.-D.); ricardo.villar@upc.edu (R.V.-R.)
Abstract:
Glass fibre is the most widely used material for reinforcing thermoplastic matrices presently
and its use continues to grow. A significant disadvantage of glass fibre, however, is its impact on the
environment, in particular, due to the fact that glass fibre-reinforced composite materials are difficult
to recycle. Polyamide 6 is an engineering plastic frequently used as a matrix for high-mechanical
performance composites. Producing polyamide monomer requires the use of a large amount of
energy and can also pose harmful environmental impacts. Consequently, glass fibre-reinforced
Polyamide 6 composites cannot be considered environmentally friendly. In this work, we assessed
the performance of a road cycling pedal body consisting of a composite of natural Polyamide 11
reinforced with lignocellulosic fibres from stone-ground wood, as an alternative to the conventional
glass fibre-reinforced Polyamide 6 composite (the most common material used for recreational
purposes). We developed a 3D model of a pedal with a geometry based on a combination of two
existing commercial choices and used it to perform three finite-element tests in order to assess its
strength under highly demanding static and cyclic conditions. A supplementary life cycle analysis
of the pedal was also performed to determine the ecological impact. Based on the results of the
simulation tests, the pedal is considered to be mechanically viable and has a significantly lower
environmental impact than fully synthetic composites.
Keywords:
natural-fibre composites; green composites; biopolymers; ecological product design;
mechanical properties; life cycle assessment
1. Introduction
Presently, 95% of all reinforced composites contain glass fibre, generating more than
7 billion dollars annually [
1
,
2
]. Composed of minerals and artificially synthesized, glass
fibre enhances the mechanical properties of polymer matrices and makes composites
lighter and stronger than their metal-based counterparts. These advantages have led to its
widespread use in the automobile, aeronautic, and sports production industries, among
others [
3
]. Ongoing research is aimed at improving the mechanical properties of glass fibre-
based composites with supplementary reinforcing materials. These new materials, referred
to as “hybrid composites” because they contain two or more reinforcements, are expected to
expand the application field of composites and increase the use and consumption of carbon
and glass fibres. However, glass fibre-based composites raise several concerns regarding
Materials 2021,14, 1399. https://doi.org/10.3390/ma14061399 https://www.mdpi.com/journal/materials
Materials 2021,14, 1399 2 of 16
safety risk assessment and environmental sustainability. Firstly, glass fibre is considered a
skin irritant material that can lead to contact dermatitis when handled [
4
,
5
]. Furthermore,
several acute respiratory health effects when glass fibre is inhaled have been reported,
including asthma, chronic airflow obstruction, and increased risk of respiratory tract
cancers [
6
–
9
]. These considerations must be considered in the manufacturing and recycling
processes. Secondly, glass fibre-based composites are not environmentally friendly and are
not easily recyclable [
10
–
12
]. The challenges associated with recycling glass fibre-based
composites have been addressed following two approaches: by developing new, more
effective recycling procedures, and by replacing composites based on mineral fibres, such
as glass, with natural fibre-reinforced polymers (NFRPs). The present research addresses
this last approach.
Natural fibres are less expensive, lighter, and less dense than synthetic fibres such as
glass or carbon; hence, they are more attractive economically [
13
]. These advantages led to
the commercialisation of synthetic fibre-reinforced polymers (SFRPs), previously based
largely on metallic materials. Natural fibres used to reinforce thermoplastic matrices are
less abrasive during material processing, provide better surface finishing with injection
moulding, are biodegradable and have minimal health impacts, and are derived from
abundant renewable sources [
14
,
15
]. However, large-scale use of NFRPs is still considered
a challenge in terms of manufacturing, especially due to the anisotropic and heterogeneous
nature of this type of material [
16
]. Replacing synthetic fibres with natural fibres is currently
regarded as an evolutionary step, an opportunity to improve mechanical performance in
reinforced composites, and a promising pathway to greater environmental sustainability.
For these reasons, there is increasing interest among scientists to expand on their potential
uses and benefits.
Thermoplastic matrices have been reinforced with fibres from cellulose-rich plants
such as flax, hemp, jute, kenaf, and sisal [
17
]. Such fibres have several environmental
advantages over synthetic fibres, but they also have some disadvantages, particularly in
terms of water uptake and mechanical impact strength. A significant amount of research
in this field has focused on assessing these two properties in NFRPs to gain a better
understanding of the influence of certain variables. The hydrophilicity of some plant
fibres and their non-cellulose components has been cited as the greatest hindrance to using
NFRPs in wet outdoor environments or under mechanically demanding conditions [
14
].
Chemically, a high cellulose content may be counterproductive and hinder the dispersion
of fibres in thermoplastic matrices [
18
]. The decreased impact strength of NFRPs relative to
synthetic fibre-reinforced composites has been attributed to increased fibre agglomeration,
increased polymer stiffness upon reinforcement, increased number of stress concentrators
around fibre ends, and contrasting hydrophilicity between the natural fibres and the
matrix [
19
]. It has been shown that the mechanical strength of NFRPs can be substantially
improved by adding an appropriate amount of a compatibilizer [
19
] for better dispersion
of reinforcing fibres in the matrix [
20
], increased adhesion between the two [
21
,
22
] and
more efficient matrix-to-fibre transfer of mechanical stress [23].
Replacing synthetic fibres with natural fibres is one approach, but it is not the only way
to obtain more sustainable composites. Another approach is to replace petroleum-based
plastic matrices with others from renewable sources such as proteins, polysaccharides,
lipids and polyesters from plants or microbes—or with materials obtained from renewable
sources [
24
]. These plastics are known as “bio-based polymers” and have gained much
scientific interest due to the increasing demand for, and scarcity of, oils [
25
], and also to the
harmful environmental impacts of conventional plastics [
26
,
27
]. Bio-based polymers, how-
ever, are still not yet used widely [
28
] due to their poor mechanical performance relative to
synthetic plastics [
29
]. Despite this, they are becoming increasingly common in biomedical,
packaging, agricultural, and food applications [
30
]. As with conventional plastics, one
approach to improve the mechanical properties of bio-based matrices is to insert reinforcing
fibres or fillers. Plastics containing natural as opposed to synthetic reinforcements are
an attractive option for environmentally friendly engineering. Some composites of this
Materials 2021,14, 1399 3 of 16
type have been shown to possess good mechanical, thermal, and electrical properties [
31
].
Additionally, bio-based production costs have gradually reduced to levels similar to those
of conventional synthetic plastics [32,33].
In this work, we adopted a case study methodology to assess mechanical performance
and industrial viability in a bicycle pedal consisting of a fully bio-based composite com-
pared to a pedal made from conventional materials. The composite materials examined
were bio-based Polyamide 11 reinforced with lignocellulosic fibres from stone-ground
wood (SGW) and a synthetic polyamide reinforced with glass fibre. A 3D model of the
pedal was generated by using a hybrid design based on two different commercial brands.
The main piece of the modelled pedal was assigned the bio-based composite, and its
mechanical performance was assessed under static and cyclic loads through computer
simulations. In order to assess the sustainability of the production of the bio-based material
in relation to its commercial counterpart, which requires careful investigation [
34
,
35
], both
were subjected to a supplementary life cycle analysis (LCA) to assess their environmental
impact in terms of raw materials, transport, production, use, and end of life [
36
]. The
carbon footprint and energy consumption for the two materials were also assessed.
The primary aims of this work were to validate theoretically the technical viability of
a fully bio-based product and to quantify the environmental benefits of its use considering
a holistic life cycle. The novelty of this work is the assessment of mechanical performance
of an environmentally friendly composite material, and an approach to advantageously re-
place composites based on technical, non-generalist matrices. Due to the fact that one of the
greatest weaknesses of natural fibre-reinforced composites is their mechanical properties,
we examined their mechanical performance under static conditions; we also performed a
novel investigation of the fatigue behaviour of the bio-based product under cyclic loadings.
In studying natural reinforced composites, it is common to analyse the thermomechanical
properties of the materials to predict their behaviour, but not to perform fatigue tests;
therefore, analysing the fatigue behaviour of the bio-based composite is also an innovative
contribution of the present research. We consider this study extension essential to assure
designers and engineers that these more sustainable and environmentally friendly materi-
als can be reliably used in new products and applications. Consequently, the hypothesis
of this research is that, for some applications, bio-based composites can replace synthetic
composites, without a loss in performance and offering several important environmental
benefits.
The remaining sections of this paper are structured as follows: Section 2describes
the methodology and specifies the materials used, Section 3presents the test results, and
Section 4reports conclusions from the test results.
2. Materials and Methods
The experimental design began with selecting the specific test target (viz., the test
case). For this purpose, we examined products used by sports professionals typically
manufactured from composites reinforced with synthetic fibres, where the plastic matrix is
an engineering plastic that can withstand relatively high mechanical stress. The aim was
not to simply select a conventional product but to confirm that a bio-based composite was a
viable choice for developing industrial products capable of fulfilling relatively demanding
application requirements. The product selected for the analysis was an automatic pedal for
road bicycles.
In terms of design, the geometry and constituent material of a product can influence
factors such as its processability and its disposal at the end of its life cycle [
37
,
38
]. Therefore,
any decisions made in these respects should be based on careful economic, social, and
environmental analyses [
39
,
40
]. The pedal studied here was a hybrid of two commercial
models: Kéo Classic 3 from Look Cycle Group (Nevers, France), and Xpresso 4 from
Time Sport International (Voreppe, France). Both were scanned on a Crysta Apex 544 3D
coordinate measuring machine from Mitutoyo (Takatsu-ku, Japan). The pedal geometry
was suitable for use with the Kéo Classic cleat from Look Cycle Group or a compatible
Materials 2021,14, 1399 4 of 16
model. A hybrid design was selected based on the primary aim of the study, which was not
to assess brands for performance but rather to use a pedal geometry as close as possible to
that of commercial models in order to examine the influence of test variables other than the
manufacturing material. The pedal was modelled using the SolidWorks 2020 software from
Dassault Systèmes (Vélizy-Villacoublay, France). Smooth integration of the test component
into the system was checked by modelling the pedal itself as well as the entire assembly.
The bio-based material used in the simulations was Polyamide 11 (PA11) reinforced
with 60 wt% natural fibres from SGW. In a previous study, this bio-based composite was
found to have similar properties to polypropylene reinforced with 20–30% of glass fibre
(S-Glass and C-Glass); however, the increased density of the bio-based polyamide resulted
in slightly worse mechanical performance in the natural composite [
41
]. The synthetic alter-
native used for comparison was a composite consisting of a Polyamide 6 matrix reinforced
with glass fibre (PA6 + GF), which is the most extensively used material in non-professional
road bicycle pedals. The proportion of reinforcing fibres used in composites differs widely
among manufacturers, accounts for 10–50% of the total pedal weight. Increasing the pro-
portion results in a linear increase in composite tensile strength [
42
], but also in increased
density—which is important since pedals should be as lightweight as possible. Due to the
large number of commercial PA6 + GF references available, we used the average values for
the technical parameters for each grade from a well-known materials library [
43
]. Table 1
lists the macroscopic mechanical properties of the materials considered. The variables
σC
t
and
σC
f
in the table denote the ultimate tensile strength and bending strength, respectively;
EC
t
and
EC
f
are the tensile and bending elastic modulus, respectively; and
εC
t
and
εC
f
are the
elongation at break under tensile and bending loads, respectively. Although the tensile
and flexural properties of the bio-based composite differed markedly from the average
values for the synthetic composites, according to the consulted material library, they were
within the ranges of values of some glass fibre-reinforced PA 6 composites, as can be seen
in
Table 2
. The tensile and flexural strengths of the bio-based material were in fact similar
to those for some low-grade composites consisting of PA6 reinforced with up to 30% of
glass fibre.
Table 1.
Tensile and flexural properties of glass fibre-reinforced Polyamide 6 composites and stone-
ground wood (SGW)-reinforced Polyamide 11 composites.
Material Tensile Properties Flexural Properties
σC
t(MPa) EC
t(GPa) εC
t(%) σC
f(MPa) EC
f(GPa) εC
f(%)
PA6 71.2 2.58 68.2 80.3 2.28 6.84
PA6 + 10% GF 92.6 4.76 5.02 140 4.2 -
PA6 + 20% GF 101 5.13 5.41 155 4.92 6.05
PA6 + 30% GF 138 7.92 4.32 207 7.41 4.86
PA6 + 40% GF 166 10.1 3.74 245 9.4 4.65
PA6 + 50% GF 195 13.9 3.06 303 12.9 3.79
PA11 38.3 1.4 25.0 40.0 0.9 7.4
PA11 + 60% SGW 59.6 5.8 2.8 102.7 4.1 3.2
Table 2. Ranges spanned by the tensile and flexural strength properties of the materials.
Material Tensile Properties Flexural Properties
n1[σC
0−σC
n] (MPa) n1[σC
0−σC
n] (MPa)
PA6 + 10% GF 54 51.7–170 167 13.8–300
PA6 + 20% GF 90 60–195 348 50–300
PA6 + 30% GF 211 50–193 676 40–800
PA6 + 40% GF 259 65–470 214 115–352
PA6 + 50% GF 202 90–605 168 175–840
1
nis the number of plastic grades per composites and intervals considered by the materials library examined [
43
].
Materials 2021,14, 1399 5 of 16
Once the characteristics of the bio-based composite were assigned to the 3D prototype
for the bio-based pedal, three finite-element numerical analyses were performed using
SolidWorks (v.2020, Dassault Systèmes, Vélizy-Villacoublay, France). A first static test
was performed to simulate cleat engagement. No maximum force for this event had
seemingly been reported, where the cyclist, with both hands on the handlebar and one
foot on the ground—or already on the other pedal—fits the cleat on the pedal. This led
us to assume a hypothetical abuse of the pedal by applying a force of 500 N to engage the
cleat. A second static test was performed to simulate the highest effective force acting on
the pedal during pedalling. The force exerted by a cyclist on a pedal changes over each
rotation cycle of the connecting rod and can be separated into an effective pedalling force
and an ineffective force along the direction of the rod [
44
,
45
]. A number of researchers
have measured the applied or effective force during pedalling with the goal of optimizing
cycling technique and performance [
44
–
51
]. The highest value reported of 1294 N was
obtained in a professional performance test under sprint conditions [
44
]. We thus used
a load of 1300 N to simulate this limiting situation. We also considered examining the
scenario in which cyclists mount or dismount a bicycle by placing their whole weight on
a pedal. This is uncommon with non-stationary bicycles and, should it occur, part of the
cyclist’s weight would fall on the handlebar. A bicycle user weighing 120 kg or less would
be unable to apply a force greater than 1300 N, therefore we assumed this scenario to be
addressed by the previous test. The last finite-element test was a fatigue analysis which
involved loading the pedal with a force of 165 N for 10
6
cycles. Considering a pedalling
cadence of 80 rpm, the force value was obtained from the average power value measured
for professional cyclists on a mountain stage of the Tour of Italy, which was 235W [
52
].
Whereas the fatigue S–N curve for a bio-based composite is not available in the literature, it
has been reported for a Polyamide 6.6 composite reinforced with 40% of glass fibre (PA6.6
+ 40%GF) [
53
,
54
]. Since the curve of interest was identical with that for non-reinforced
PA6.6—the ductile matrix prevails in the fatigue behaviour of composites with strong
fibre–matrix bonds [
55
]—and PA11 has much better fatigue properties than PA6.6 [
56
,
57
],
the behaviour of the bio-based composite was conservatively assumed to be similar to that
of the petroleum-derived composite, which limited the scope of the study.
The environmental and commercial implications of the bio-based material were com-
pared with those of the commercial composite in an LCA by using the sustainability
module in SolidWorks 2020 under the assumption that the pedal would be manufactured
and recycled in Europe. The geometry used was that of the hybrid pedal’s main body,
which was assumed to consist of the materials shown in Table 1.
3. Results
3.1. Definition of the Case Study
As discussed above, the test case was the main body of an automatic bicycle pedal.
This type of pedal enables more efficient pedalling than the classical model by virtue of a
pedal–shoe interface that results in more effective pedalling force during each rotation of
the connecting rod. Automatic pedals are widely used among professional road cyclists
and extensively used by recreational bikers. The cyclist’s shoe fits the pedal through a
piece called a “cleat” that is screwed onto the shoe. Generally, the pedal components in
contact with the cleat are made of a composite reinforced with synthetic fibres, whereas
the cleat consists of non-reinforced thermoplastic material (e.g., polyacetal in the Kéo Look
model cleat).
Figure 1shows the hybrid pedal with the cleat off and on. Although mechanical
computations were based on professional performance data, the target user was an amateur
cyclist. The cleat was designed to be compatible with the Kéo Look model, which is
something usual among manufacturers of other brands. An automatic pedal is comprised
of the following components (Figure 2): main body; cleat-pedal locking part; steel axle,
which is screwed to the connecting rod and receives pedalling forces via two bearings; and
a carbon fibre sheet that acts as a spring to hold the main body-lock pair together. The
Materials 2021,14, 1399 6 of 16
cyclist’s shoe can be easily fitted on the pedal by placing the cleat front over the pedal hole
and pressing slightly upwards to have the cleat retained. Conversely, rotating the foot to
move the heel away from the bicycle’s vertical plane causes the spring to give and allows
the foot to be detached from the pedal.
Materials 2021, 14, x FOR PEER REVIEW 6 of 17
and extensively used by recreational bikers. The cyclist’s shoe fits the pedal through a
piece called a “cleat” that is screwed onto the shoe. Generally, the pedal components in
contact with the cleat are made of a composite reinforced with synthetic fibres, whereas
the cleat consists of non-reinforced thermoplastic material (e.g., polyacetal in the Kéo Look
model cleat).
Figure 1 shows the hybrid pedal with the cleat off and on. Although mechanical com-
putations were based on professional performance data, the target user was an amateur
cyclist. The cleat was designed to be compatible with the Kéo Look model, which is some-
thing usual among manufacturers of other brands. An automatic pedal is comprised of
the following components (Figure 2): main body; cleat-pedal locking part; steel axle,
which is screwed to the connecting rod and receives pedalling forces via two bearings;
and a carbon fibre sheet that acts as a spring to hold the main body-lock pair together. The
cyclist’s shoe can be easily fitted on the pedal by placing the cleat front over the pedal hole
and pressing slightly upwards to have the cleat retained. Conversely, rotating the foot to
move the heel away from the bicycle’s vertical plane causes the spring to give and allows
the foot to be detached from the pedal.
(a) (b)
Figure 1. Proposed hybrid pedal design. (a) Cleat off; (b) cleat on.
Figure 2. Exploded view of the pedal.
Unlike commercial models, the main body of the hybrid pedal consisted of a bio-
based PA11 + 60% SGW composite rather than glass fibre-reinforced PA6 as in amateur
Figure 1. Proposed hybrid pedal design. (a) Cleat off; (b) cleat on.
Materials 2021, 14, x FOR PEER REVIEW 6 of 17
and extensively used by recreational bikers. The cyclist’s shoe fits the pedal through a
piece called a “cleat” that is screwed onto the shoe. Generally, the pedal components in
contact with the cleat are made of a composite reinforced with synthetic fibres, whereas
the cleat consists of non-reinforced thermoplastic material (e.g., polyacetal in the Kéo Look
model cleat).
Figure 1 shows the hybrid pedal with the cleat off and on. Although mechanical com-
putations were based on professional performance data, the target user was an amateur
cyclist. The cleat was designed to be compatible with the Kéo Look model, which is some-
thing usual among manufacturers of other brands. An automatic pedal is comprised of
the following components (Figure 2): main body; cleat-pedal locking part; steel axle,
which is screwed to the connecting rod and receives pedalling forces via two bearings;
and a carbon fibre sheet that acts as a spring to hold the main body-lock pair together. The
cyclist’s shoe can be easily fitted on the pedal by placing the cleat front over the pedal hole
and pressing slightly upwards to have the cleat retained. Conversely, rotating the foot to
move the heel away from the bicycle’s vertical plane causes the spring to give and allows
the foot to be detached from the pedal.
(a) (b)
Figure 1. Proposed hybrid pedal design. (a) Cleat off; (b) cleat on.
Figure 2. Exploded view of the pedal.
Unlike commercial models, the main body of the hybrid pedal consisted of a bio-
based PA11 + 60% SGW composite rather than glass fibre-reinforced PA6 as in amateur
Figure 2. Exploded view of the pedal.
Unlike commercial models, the main body of the hybrid pedal consisted of a bio-based
PA11 + 60% SGW composite rather than glass fibre-reinforced PA6 as in amateur pedals.
The main body of an automatic pedal is the component under the greatest loading during
pedalling; therefore, it was selected as the component to be simulated. The locking part
could be made from the same material; in addition, all other components were made of the
same materials as those used in automatic pedals for amateur cycling.
Materials 2021,14, 1399 7 of 16
3.2. Analysis of the Test Case
As stated in Section 2, the finite-element tests were conducted using SolidWorks 2020
(specifically, with the simulation module available in the premium version). Two different
static scenarios were considered: cleat engagement and pedalling. A third scenario was
examined in order to assess the fatigue effects on the pedal’s main body which are produced
by the cyclical loads applied during pedalling. Mechanical analyses were extended to
the main body and steel axle (i.e., the element conveying loads), in order to simulate a
more realistic contour condition as the axle is a deformable element over which the loads
are distributed. In the static tests, the pedal was assumed to be a fixed element, and
motion in the engagement zone was restricted. Loads were uniformly distributed over the
surfaces of the pedal’s main body in contact with the cleat at the time a load was applied
by the user. Both static analyses used a 10-node quadratic tetrahedral element mesh, with
75,328 elements and an average size of 1.667
±
0.0833 mm. Precision was improved by
refining the mesh in those zones under increased solicitation (viz., 16 sides of the pedal
body geometry). The aspect ratio was greater than 3 in more than 98.3% of the elements.
The outputs of the static finite-element tests were Von Mises stress (MPa), net displacement
(mm), and strains (%), all with their corresponding colour maps on the 3D model.
Engaging the cleat requires the cyclist to apply a slight force over a highly specific zone
in the front of the pedal body (Figure 3a). When the cleat comes into contact with the pedal
locking part, the spring gives and shifts the piece backwards. Once the cleat is properly
placed on the pedal, the locking part returns to its initial position to ensure coupling of
the cleat–pedal pair. The sheet acting as a spring during engagement of the cleat allows a
relative movement between both components, reducing the stress analysis to the pressure
exerted by contact between the cleat and the pedal’s body. Although the cleat can be
engaged by applying a minimal force, it can be difficult for cyclists not used to automatic
pedals to perform this action, and can even cause them to fall; in extreme situations, this
can generate considerable loads on the surface of the pedal’s main body in contact with the
cleat at the beginning of the engagement process. As no study has evaluated the effect of
the load applied during the engagement operation, we used a conservative load of 500 N
to represent a scenario of extreme misuse. Figure 3shows the results of the finite element
analysis in the engagement scenario between the cleat and the pedal. The maximum Von
Mises stress obtained was 30.05 MPa, which is approximately half of the tensile strength of
the composite, while the maximum displacement was 0.14 mm. The results indicate that
there is no possibility of breakage of the piece under the conditions of analysis. Similarly,
the small deformation values show that the bio-based composite has sufficient rigidity and
the deformations that occur will not affect the functioning of the part.
The loaded surface differs between the cleat engagement and pedalling operations
because, in the latter, the cleat is in contact with the central part of the pedal’s main body.
Due to the fact that the cleat is anchored to the pedal, the surface over which the force
is exerted is independent of the rotation angle of the part. In contrast, the applied force
and effective force are dependent on the rotation angle of the connecting rod. As stated
in Section 2, we used a force of 1300 N—slightly larger than the highest measured value
in previous studies—in the static analysis of the pedalling scenario. As can be seen in
Figure 4a, the load was uniformly distributed over the central part of the pedal’s main
body. The highest stress of 33 MPa was located at the contact point with the radial ball
bearing (Figure 4b), which is 44% lower than the ultimate tensile strength of the bio-based
composite, resulting in a conservative safety factor of approximately 1.8. Consequently,
the applied force would be unable to cause material failure. Regarding the deformation,
the analysis determined a maximum displacement of 0.29 mm located on the opposite
end of the connection between the pedal and the crank (Figure 4c). In contrast, the strain,
although small, is focused on the most stressed region which is located at the end where
the pedal and connecting rod are joined (Figure 4d). Figure 4e illustrates pedal-to-axle load
transmission; as can be seen, the axle played a central role in the mechanical response of
the pedal’s main body.
Materials 2021,14, 1399 8 of 16
Materials 2021, 14, x FOR PEER REVIEW 8 of 17
(a) (b)
(c) (d)
Figure 3. Graphic output summaries of the finite-element analysis of a PA11 + 60% SGW pedal body during cleat engage-
ment under extreme use conditions. (a) Loaded surface; (b) Von Mises stress; (c) net displacement; (d) percent strain.
The loaded surface differs between the cleat engagement and pedalling operations
because, in the latter, the cleat is in contact with the central part of the pedal’s main body.
Due to the fact that the cleat is anchored to the pedal, the surface over which the force is
exerted is independent of the rotation angle of the part. In contrast, the applied force and
effective force are dependent on the rotation angle of the connecting rod. As stated in
Section 2, we used a force of 1300 N—slightly larger than the highest measured value in
previous studies—in the static analysis of the pedalling scenario. As can be seen in Figure
4a, the load was uniformly distributed over the central part of the pedal’s main body. The
highest stress of 33 MPa was located at the contact point with the radial ball bearing (Fig-
ure 4b), which is 44% lower than the ultimate tensile strength of the bio-based composite,
resulting in a conservative safety factor of approximately 1.8. Consequently, the applied
force would be unable to cause material failure. Regarding the deformation, the analysis
determined a maximum displacement of 0.29 mm located on the opposite end of the con-
nection between the pedal and the crank (Figure 4c). In contrast, the strain, although small,
is focused on the most stressed region which is located at the end where the pedal and
connecting rod are joined (Figure 4d). Figure 4e illustrates pedal-to-axle load transmis-
sion; as can be seen, the axle played a central role in the mechanical response of the pedal’s
main body.
Figure 3.
Graphic output summaries of the finite-element analysis of a PA11 + 60% SGW pedal body during cleat engagement
under extreme use conditions. (a) Loaded surface; (b) Von Mises stress; (c) net displacement; (d) percent strain.
As the load is applied cyclically every pedal stroke, the fatigue behaviour of the
pedal’s main body during pedalling is another valuable subject for analysis. This fatigue
analysis is actually critical since, at 80 rpm (a typical but conservative pedalling rate),
a cyclist can generate 4800 full turns of the connecting rod in an hour. In other words,
with the static analysis carried out previously, it would be insufficient to characterize and
validate the response of the bio-based composite applied to the geometry of the pedal’s
main body. To standardise the fatigue analysis, 10
6
cycles were applied, with cyclical
stresses of constant amplitude, a stress ratio equal to 0, and a single event (SolidWorks
parameters). The new finite-element analysis was conducted by applying a load of 165 N to
the central portion of the designed pedal’s main body, which is the average pedalling force
measured on a mountain stage of the Tour of Italy at a cadence of 80 rpm [
52
]. As stated
in Section 2, the S–N curve used as input for computations on the bio-based material was
assumed to be identical with that for PA6 + 40% GF (Figure 5). The S-N curve suggests that
after 10
6
cycles, the mechanical properties of the material will not deteriorate substantially,
so it is possible to interpret the results as the material having infinite life. As can be seen in
Figure 6, the part withstood 10
6
cycles with negligible impact, since no point on the mesh
has a load factor lower than unity. In fact, the minimum load factor obtained in the analysis
is above 5, indicating that the material properties were effectively unchanged. Therefore, it
Materials 2021,14, 1399 9 of 16
can be concluded that the part would be able to withstand a much higher number of cycles;
this is further evidenced by the fact that conservative values were used in the analysis.
Materials 2021, 14, x FOR PEER REVIEW 9 of 17
(a) (b)
(c) (d)
(e)
Figure 4. Graphic output summaries of the finite-element analysis of a PA11 + 60% SGW pedal body during pedalling
under a force of 1300 N. (a) Loaded surface; (b) Von Mises stress; (c) net displacement; (d) percent strain; (e) effort trans-
mission to axle.
As the load is applied cyclically every pedal stroke, the fatigue behaviour of the pe-
dal’s main body during pedalling is another valuable subject for analysis. This fatigue
analysis is actually critical since, at 80 rpm (a typical but conservative pedalling rate), a
cyclist can generate 4800 full turns of the connecting rod in an hour. In other words, with
the static analysis carried out previously, it would be insufficient to characterize and val-
idate the response of the bio-based composite applied to the geometry of the pedal’s main
body. To standardise the fatigue analysis, 106 cycles were applied, with cyclical stresses of
constant amplitude, a stress ratio equal to 0, and a single event (SolidWorks parameters).
The new finite-element analysis was conducted by applying a load of 165 N to the central
portion of the designed pedal’s main body, which is the average pedalling force measured
on a mountain stage of the Tour of Italy at a cadence of 80 rpm [52]. As stated in Section
Figure 4.
Graphic output summaries of the finite-element analysis of a PA11 + 60% SGW pedal body during pedalling under
a force of 1300 N. (
a
) Loaded surface; (
b
) Von Mises stress; (
c
) net displacement; (
d
) percent strain; (
e
) effort transmission
to axle.
Materials 2021,14, 1399 10 of 16
Materials 2021, 14, x FOR PEER REVIEW 10 of 17
2, the S–N curve used as input for computations on the bio-based material was assumed
to be identical with that for PA6 + 40% GF (Figure 5). The S-N curve suggests that after 106
cycles, the mechanical properties of the material will not deteriorate substantially, so it is
possible to interpret the results as the material having infinite life. As can be seen in Figure
6, the part withstood 106 cycles with negligible impact, since no point on the mesh has a
load factor lower than unity. In fact, the minimum load factor obtained in the analysis is
above 5, indicating that the material properties were effectively unchanged. Therefore, it
can be concluded that the part would be able to withstand a much higher number of cy-
cles; this is further evidenced by the fact that conservative values were used in the analy-
sis.
Figure 5. Normalized S-N curve assigned to the PA11 + 60% SGW composite. Adapted from [53].
Figure 6. Part load factor due to the simulated cyclical event.
3.3. Life Cycle Analysis
It is understood that a fully bio-based composite should have a lesser environmental
impact than that of a conventional synthetic composite. In this study, the thermoplastic
matrix of the bio-based composite was obtained from the castor bean, a ricin oil-rich plant;
in addition, the typical high-density (2.48 g/cm3) synthetic glass fibre was replaced with a
lower density (1.34 g/cm3) natural alternative (SGW fibres). As a result, the bio-based ma-
terial was expected to be more environmentally friendly than the synthetic material. The
order of magnitude of the potential gains in environmental impacts was estimated using
the sustainability module in SolidWorks 2020, to compare the two types of material
0.0
0.2
0.4
0.6
0.8
1.0
1.2
01234567
Normalized composite stress
amplitude
Cycles to failure, N, (log)
Normalized S–N data for an unreinforced PA66
and a 40% short glass fiber PA66
Figure 5. Normalized S-N curve assigned to the PA11 + 60% SGW composite. Adapted from [53].
Materials 2021, 14, x FOR PEER REVIEW 10 of 17
2, the S–N curve used as input for computations on the bio-based material was assumed
to be identical with that for PA6 + 40% GF (Figure 5). The S-N curve suggests that after 106
cycles, the mechanical properties of the material will not deteriorate substantially, so it is
possible to interpret the results as the material having infinite life. As can be seen in Figure
6, the part withstood 106 cycles with negligible impact, since no point on the mesh has a
load factor lower than unity. In fact, the minimum load factor obtained in the analysis is
above 5, indicating that the material properties were effectively unchanged. Therefore, it
can be concluded that the part would be able to withstand a much higher number of cy-
cles; this is further evidenced by the fact that conservative values were used in the analy-
sis.
Figure 5. Normalized S-N curve assigned to the PA11 + 60% SGW composite. Adapted from [53].
Figure 6. Part load factor due to the simulated cyclical event.
3.3. Life Cycle Analysis
It is understood that a fully bio-based composite should have a lesser environmental
impact than that of a conventional synthetic composite. In this study, the thermoplastic
matrix of the bio-based composite was obtained from the castor bean, a ricin oil-rich plant;
in addition, the typical high-density (2.48 g/cm3) synthetic glass fibre was replaced with a
lower density (1.34 g/cm3) natural alternative (SGW fibres). As a result, the bio-based ma-
terial was expected to be more environmentally friendly than the synthetic material. The
order of magnitude of the potential gains in environmental impacts was estimated using
the sustainability module in SolidWorks 2020, to compare the two types of material
0.0
0.2
0.4
0.6
0.8
1.0
1.2
01234567
Normalized composite stress
amplitude
Cycles to failure, N, (log)
Normalized S–N data for an unreinforced PA66
and a 40% short glass fiber PA66
Figure 6. Part load factor due to the simulated cyclical event.
3.3. Life Cycle Analysis
It is understood that a fully bio-based composite should have a lesser environmental
impact than that of a conventional synthetic composite. In this study, the thermoplastic
matrix of the bio-based composite was obtained from the castor bean, a ricin oil-rich plant;
in addition, the typical high-density (2.48 g/cm
3
) synthetic glass fibre was replaced with
a lower density (1.34 g/cm
3
) natural alternative (SGW fibres). As a result, the bio-based
material was expected to be more environmentally friendly than the synthetic material. The
order of magnitude of the potential gains in environmental impacts was estimated using
the sustainability module in SolidWorks 2020, to compare the two types of material through
LCA. Like similar commercial software tools, SolidWorks performs weighted computations
and does not account for important design and manufacturing characteristics, which
limits its usefulness [
58
]; for this reason, the results of the analysis were considered to
be estimates.
The analysis focused on the pedal’s main body and excluded all other elements of the
proposed automatic pedal. Table 3lists the materials used in the simulations. All materials
were assumed to be “pure” (i.e., they contained no recycled products). Additionally, the
complete life cycle, from the raw materials to the product’s end-of-life, was assumed to
occur in Europe. In addition, the pedal was assumed to have a life span of 10 years, to have
Materials 2021,14, 1399 11 of 16
been manufactured by electrical injection moulding (IM), and to have been carried in a
lorry over a distance of 2000 km on average.
Table 3. Selected properties of pedals consisting of various composites.
Property Density (g/cm3)Weight (g) Resin Volume (%) Fibre Volume (%)
PA6 1.12 33.17 100 -
PA6 + 10% GF 1.18 35.09 95.22 4.78
PA6 + 20% GF 1.26 37.25 89.86 10.14
PA6 + 30% GF 1.34 39.70 83.78 16.22
PA6 + 40% GF 1.43 42.49 76.86 23.14
PA6 + 50% GF 1.54 45.70 68.89 31.11
PA11 1.03 30.50 100 -
PA11 + 60% SGW 1.20 35.42 46.45 53.50
Although IM with fully electrical equipment is among the most energy-efficient
manufacturing processes [
59
], its specific energy consumption (SEC) influences the carbon
footprint and amount of energy consumed in the overall process and is thus an interesting
feature. SEC is influenced by various factors including the nature of the injected material,
screw rate, back-pressure, and residence time [
60
]. In practice, SEC is often taken as
1.47 kWh/kg, which is the average value in the EcoInvest database. Due to the fact that the
value for polyamide is known to be greater, we used its value of 1.68 kWh/kg for PA6 in
SolidWorks. The choice of SEC for electrical IM is important because SEC is known to be
greater for synthetic fibres and pure polymers than it is for composites of lignocellulosic
fibres—which have lower melting points and require lower energy to avoid damage during
moulding [
61
]. Therefore, using the previous SEC value would have underestimated the
potential of the bio-based composite.
The LCA was performed on the product under the assumption that PA6-based materi-
als have a potential recyclability of 25% and a dumping rate of 51%. This is a favourable
assumption for the current glass fibre recyclability, even if recent advances in recycling
procedures are considered [
10
,
62
]. Based on previous reports [
41
], the PA11-based materials
were assigned 60% recyclability, 30% ashing, and 10% dumping.
As the pedal materials were assumed to be obtained separately, the LCA excluded the
energy required for matrix–fibre mixing of the composites. As a result, their overall carbon
footprint and energy consumption were underestimated. However, this did not preclude
comparing the bio-based and synthetic composites since both were similarly affected in
this respect.
Based on the carbon footprint data in Figure 7and Table 4, increasing the propor-
tion of reinforcing material in the synthetic composite led to increased CO
2
emissions;
the increase, while moderate, occurred throughout the life cycle (obtainment of the raw
material, manufacturing, transport, and end of life). PA6 production has a strong impact
on CO
2
emissions and glass fibre increases the impact slightly. Likely due to the release of
various gaseous pollutants during the glass fibre production process, the emission factor of
this material is penalised, since the energy consumption is not higher, as seen in
Figure 8
.
In practice, the higher the proportion of glass fibre, the higher the melting point of the
composite and the greater the energy needed for plasticization. Glass fibre also increases
the viscosity of the resulting composite and requires using a higher injection pressure [
61
].
In summary, the results of the LCA analysis align with the expected outcomes for the
production process: increasing the proportion of glass fibre increased composite density
and pedal weight (Table 3), resulting in an increased impact on carbon footprint at the
transport and end-of-life stages.
Materials 2021,14, 1399 12 of 16
Materials 2021, 14, x FOR PEER REVIEW 12 of 17
composite and the greater the energy needed for plasticization. Glass fibre also increases
the viscosity of the resulting composite and requires using a higher injection pressure [61].
In summary, the results of the LCA analysis align with the expected outcomes for the
production process: increasing the proportion of glass fibre increased composite density
and pedal weight (Table 3), resulting in an increased impact on carbon footprint at the
transport and end-of-life stages.
Figure 7. Carbon footprint for a pedal with a 10-year lifespan.
Due to the fact that PA11 is not included in the database of the sustainability module
of SolidWorks, and the fact that this software does not allow the creation of new entries,
the material was assumed to have the same properties as PA6, and the pedal volume was
altered to have the same density as PA11. This was another conservative assumption since
PA11 production does not increase atmospheric CO2 emissions because the equivalent
amount of CO2 is absorbed during new plant growth; in addition, the consumption energy
for PA11 production is lower than that for any other polyamide [63]. As a result, the LCA
significantly overestimated the carbon footprint for the proposed pedal with a bio-based
polymer matrix. Even so, as shown in Figure 7, producing a pedal body of bio-based com-
posite is clearly more environmentally sustainable than producing synthetic alternatives.
Table 4. Carbon footprint (kg CO2) by composite and life cycle analysis (LCA) stage with a life expectancy of 10 years.
Stage PA6 PA6 + 10% GF PA6 + 20% GF PA6 + 30% GF PA6 + 40% GF PA6 + 50% GF PA11 PA11 + 60%
SGW
Material 0.340 0.344 0.347 0.351 0.357 0.361 0.313 0.170
Manufacture 0.035 0.038 0.040 0.043 0.045 0.048 0.033 0.038
Transport 0.003 0.003 0.004 0.004 0.004 0.004 0.003 0.004
End of life 0.022 0.023 0.025 0.027 0.028 0.030 0.014 0.020
Total 0.400 0.408 0.415 0.425 0.434 0.443 0.363 0.231
The energy consumption results of the LCA showed a similar trend to the carbon
footprint results. Thus, the bio-based composite was the most environmentally friendly
option (see Figure 8 and Table 5), and also the most economical. In fact, production of
non-reinforced PA6 monomer accounts for 90% of the entire energy consumption. It
should be noted that most of the energy required for IM manufacturing is used to obtain
the raw material and manufacture the product, with the former consuming three times
more energy than the latter [64]. In our case, producing non-reinforced PA6 would have
required almost 10 times more energy than manufacturing the pedal, which indicates the
strong influence of the particular polyamide on the energy consumption estimates. Alt-
hough the results suggest that energy consumption with the synthetic materials decreases
as the proportion of fibre increases, the energy of mixing the two components was not
considered, so the actual amount of energy to be used would likely increase with an in-
creasing proportion of fibre. Despite this, comparing the energy consumption and carbon
0
0.1
0.2
0.3
0.4
0.5
PA6 PA6 + 10%
GF
PA6 + 20%
GF
PA6 + 30%
GF
PA6 + 40%
GF
PA6 + 50%
GF
PA11 PA11 +
60% SGW
Carbon Footprint (kgCO2e)
Material Manufacturing Transport End of Life
Figure 7. Carbon footprint for a pedal with a 10-year lifespan.
Table 4. Carbon footprint (kg CO2) by composite and life cycle analysis (LCA) stage with a life expectancy of 10 years.
Stage PA6 PA6 + 10% GF PA6 + 20% GF PA6 + 30% GF PA6 + 40% GF PA6 + 50% GF PA11 PA11 + 60% SGW
Material
0.340
0.344 0.347 0.351 0.357 0.361
0.313
0.170
Manufacture
0.035
0.038 0.040 0.043 0.045 0.048
0.033
0.038
Transport
0.003
0.003 0.004 0.004 0.004 0.004
0.003
0.004
End of life
0.022
0.023 0.025 0.027 0.028 0.030
0.014
0.020
Total
0.400
0.408 0.415 0.425 0.434 0.443
0.363
0.231
Materials 2021, 14, x FOR PEER REVIEW 13 of 17
footprint results reveals that glass fibre production has a stronger impact on the latter than
on the former. This is a result of the increased emission of pollutants in the production
process [65] despite the more efficient energy use [66]. In the other LCA stages, for the
same reasons as the carbon footprint, energy consumption increased with increasing pro-
portion of glass fibre. Additionally, the low energy consumption of the bio-based compo-
site was due to the decreased proportion of polyamide and the use of a fibre type with
lower energy requirements than fibre glass and polyamide. In summary, using the bio-
based composite could save approximately 3 MJ with respect to synthetic composites.
Figure 8. Energy consumption over a 10-year life cycle.
Table 5. Energy consumption (MJ) by LCA stage for various materials with a life expectancy of 10 years.
Stage PA6
PA6 + 10%
GF
PA6 + 20%
GF
PA6 + 30%
GF
PA6 + 40%
GF
PA6 + 50%
GF PA11 PA11 + 60%
SGW
Material 6.200 6.117 6.058 5.933 5.800 5.700 5.700 3.036
Manufacture 0.673 0.712 0.756 0.805 0.862 0.927 0.619 0.702
Transport 0.046 0.049 0.052 0.056 0.060 0.064 0.043 0.052
End of life 0.017 0.018 0.019 0.020 0.022 0.022 0.011 0.012
Total 6.936 6.896 6.885 6.814 6.744 6.713 6.373 3.802
The benefit in terms of carbon footprint and energy consumption is significant, in
contrast to other recent research in which SGW-reinforced PA11 did not represent a great
advantage [41]. It can be reasoned that the environmental benefit of bio-based composites
is achieved when they replace technical composites that use matrices such as PA6 or sim-
ilar. In this sense, if the mechanical properties of the fully bio-based composite were su-
perior, it would be expected that it would replace synthetic materials in more applications.
Consequently, it would be advantageous to improve these properties, for example, with
the use of reactive coupling agents (from biological origin, if possible).
4. Conclusions
The superior material properties of glass fibre-reinforced composites are well known.
Depending on the nature of the glass fibres, their size, and their orientation in the thermo-
plastic matrix, a composite can have good mechanical, chemical, and electrical insulation
properties in addition to low weight and cost. However, glass fibres are known to pose
serious environmental problems arising from the low recyclability of their widely used
composites. In response, scientists are developing new procedures to increase their recy-
cling or replace the reinforcing material for easier reuse. Both areas of research are ad-
vancing at a promising pace.
Natural fibres constitute an effective alternative to synthetic raw materials such as
glass fibres. Natural fibres are less expensive, lighter, and less dense than synthetic fibres;
0
1
2
3
4
5
6
7
8
PA6 PA6 + 10%
GF
PA6 + 20%
GF
PA6 + 30%
GF
PA6 + 40%
GF
PA6 + 50%
GF
PA11 PA11 +
60% SGW
Energy Consumption (MJ)
Material Manufacturing Transport End of Life
Figure 8. Energy consumption over a 10-year life cycle.
Due to the fact that PA11 is not included in the database of the sustainability module
of SolidWorks, and the fact that this software does not allow the creation of new entries,
the material was assumed to have the same properties as PA6, and the pedal volume was
altered to have the same density as PA11. This was another conservative assumption since
PA11 production does not increase atmospheric CO
2
emissions because the equivalent
amount of CO
2
is absorbed during new plant growth; in addition, the consumption energy
for PA11 production is lower than that for any other polyamide [63]. As a result, the LCA
significantly overestimated the carbon footprint for the proposed pedal with a bio-based
polymer matrix. Even so, as shown in Figure 7, producing a pedal body of bio-based com-
posite is clearly more environmentally sustainable than producing synthetic alternatives.
Materials 2021,14, 1399 13 of 16
The energy consumption results of the LCA showed a similar trend to the carbon
footprint results. Thus, the bio-based composite was the most environmentally friendly
option (see Figure 8and Table 5), and also the most economical. In fact, production of
non-reinforced PA6 monomer accounts for 90% of the entire energy consumption. It should
be noted that most of the energy required for IM manufacturing is used to obtain the raw
material and manufacture the product, with the former consuming three times more energy
than the latter [
64
]. In our case, producing non-reinforced PA6 would have required almost
10 times more energy than manufacturing the pedal, which indicates the strong influence
of the particular polyamide on the energy consumption estimates. Although the results
suggest that energy consumption with the synthetic materials decreases as the proportion
of fibre increases, the energy of mixing the two components was not considered, so the
actual amount of energy to be used would likely increase with an increasing proportion
of fibre. Despite this, comparing the energy consumption and carbon footprint results
reveals that glass fibre production has a stronger impact on the latter than on the former.
This is a result of the increased emission of pollutants in the production process [
65
]
despite the more efficient energy use [
66
]. In the other LCA stages, for the same reasons as
the carbon footprint, energy consumption increased with increasing proportion of glass
fibre. Additionally, the low energy consumption of the bio-based composite was due
to the decreased proportion of polyamide and the use of a fibre type with lower energy
requirements than fibre glass and polyamide. In summary, using the bio-based composite
could save approximately 3 MJ with respect to synthetic composites.
Table 5. Energy consumption (MJ) by LCA stage for various materials with a life expectancy of 10 years.
Stage PA6 PA6 + 10% GF PA6 + 20% GF PA6 + 30% GF PA6 + 40% GF PA6 + 50% GF PA11 PA11 + 60% SGW
Material
6.200
6.117 6.058 5.933 5.800 5.700
5.700
3.036
Manufacture
0.673
0.712 0.756 0.805 0.862 0.927
0.619
0.702
Transport
0.046
0.049 0.052 0.056 0.060 0.064
0.043
0.052
End of life
0.017
0.018 0.019 0.020 0.022 0.022
0.011
0.012
Total
6.936
6.896 6.885 6.814 6.744 6.713
6.373
3.802
The benefit in terms of carbon footprint and energy consumption is significant, in
contrast to other recent research in which SGW-reinforced PA11 did not represent a great
advantage [
41
]. It can be reasoned that the environmental benefit of bio-based composites
is achieved when they replace technical composites that use matrices such as PA6 or
similar. In this sense, if the mechanical properties of the fully bio-based composite were
superior, it would be expected that it would replace synthetic materials in more applications.
Consequently, it would be advantageous to improve these properties, for example, with
the use of reactive coupling agents (from biological origin, if possible).
4. Conclusions
The superior material properties of glass fibre-reinforced composites are well known.
Depending on the nature of the glass fibres, their size, and their orientation in the thermo-
plastic matrix, a composite can have good mechanical, chemical, and electrical insulation
properties in addition to low weight and cost. However, glass fibres are known to pose
serious environmental problems arising from the low recyclability of their widely used
composites. In response, scientists are developing new procedures to increase their re-
cycling or replace the reinforcing material for easier reuse. Both areas of research are
advancing at a promising pace.
Natural fibres constitute an effective alternative to synthetic raw materials such as
glass fibres. Natural fibres are less expensive, lighter, and less dense than synthetic fibres;
in addition, they are biodegradable, and hence offer environmental and economic benefits.
Mechanically, however, natural fibres are less resistant to impact; they are also more
hydrophilic than synthetic materials. These material properties are important for glass
fibre-reinforced composites.
Materials 2021,14, 1399 14 of 16
In this work, we used finite-element simulations to estimate the mechanical suitability
of a bicycle pedal part made from a fully bio-based composite consisting of a natural
polyamide (PA11) matrix reinforced with 60 wt% lignocellulosic fibre from SGW. The
simulation results indicate the product is mechanically feasible. Based on the nature of
the finite-element simulations, it is advisable to assess the performance of the pedal under
real-life conditions.
From an environmental standpoint, the preliminary analysis of the life cycle of the
product showed considerable benefits in terms of carbon footprint and energy consumed.
Specifically, the estimates indicated reductions in the impact of the carbon footprint and
energy consumption of more than 40% with the use of the bio-based composite.
Therefore, it is theoretically demonstrated that fully bio-based technical composites
can replace synthetic composites in certain applications, and that the environmental benefits
can be high. Future improvements in the mechanical properties of PA11 + 60%SGW would
enable more widespread use and increase its environmental benefits.
Author Contributions:
D.H.-D. was responsible for carrying out the life cycle analysis, writing the
manuscript, and editing the images. R.V.-R. created the 3D pedal model and performed the finite
element simulations. F.S.-P. participated in advising on synthetic and bio-based composite materials,
and validated the technical characteristics presented. R.W.-P. and M.S.-R. advised on the methodology
of finite element tests and the interpretation of their results. J.I.R.-S. and F.J. conceptualized, designed
the experimental methodology, coordinated and supervised the entire study. 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: There is no additional data.
Acknowledgments:
The authors thank the anonymous reviewers, whose constructive comments
helped us to improve the paper.
Conflicts of Interest: The authors declare no conflict of interest.
References
1. Thomason, J. Glass fibre sizing: A review. Compos. Part A Appl. Sci. Manuf. 2019,127, 105619. [CrossRef]
2.
Singh, J.; Kumar, M.; Kumar, S.; Mohapatra, S.K. Properties of Glass-Fiber Hybrid Composites: A Review. Polym. Technol. Eng.
2016,56, 455–469. [CrossRef]
3.
Kanitkar, Y.M.; Kulkarni, A.P.; Wangikar, K.S. Characterization of Glass Hybrid composite: A Review. Mater. Today Proc.
2017
,4,
9627–9630. [CrossRef]
4.
Tarvainen, K.; Jolanki, R.; Forsman-Grönholm, L.; Estlander, T.; Pfäffli, P.; Juntunen, J.; Kanerva, L. Exposure, skin protection and
occupational skin diseases in the glass-fibre-reinforced plastics industry. Contact Dermat. 1993,29, 119–127. [CrossRef]
5.
Hogan, D.J.; Morrison, M.; Desai, A. Fiberglass, Dusts. In Kanerva’s Occupational Dermatology; Springer International Publishing:
New York, NY, USA, 2019; pp. 543–557.
6.
Milton, D.K.; Walters, M.D.; Hammond, K.; Evans, J.S. Worker exposure to endotoxin, phenolic compounds, and formal-dehyde
in a fiberglass insulation manufacturing plant. Am. Ind. Hyg. Assoc. J. 1996,57, 889–896. [CrossRef]
7.
Costa, R.; Orriols, R. Man-Made Mineral Fibers and the Respiratory Tract. Arch. Bronconeumol.
2012
,48, 460–468. [CrossRef]
[PubMed]
8.
Baan, R.A.; Grosse, Y. Man-made mineral (vitreous) fibres: Evaluations of cancer hazards by the IARC Monographs Pro-gramme.
Mutat. Res. 2004,553, 43–58. [CrossRef]
9.
Kwak, K.; Paek, D.; Park, J. Occupational exposure to formaldehyde and risk of lung cancer: A systematic review and meta-
analysis. Am. J. Ind. Med. 2020,63, 312–327. [CrossRef] [PubMed]
10.
Rahimizadeh, A.; Kalman, J.; Fayazbakhsh, K.; Lessard, L. Recycling of fiberglass wind turbine blades into reinforced fila-ments
for use in Additive Manufacturing. Compos. Part B Eng. 2019,175, 107101. [CrossRef]
11.
Ciocan, C.; Kristova, P.; Annels, C.; Derjean, M.; Hopkinson, L. Glass reinforced plastic (GRP) a new emerging contaminant—First
evidence of GRP impact on aquatic organisms. Mar. Pollut. Bull. 2020,160, 111559. [CrossRef]
12.
Castro, A.C.M.; Carvalho, J.P.; Ribeiro, M.C.S.; Meixedo, J.P.; Silva, F.J.; Fiúza, A.; Dinis, M.D.L. An integrated recycling approach
for GFRP pultrusion wastes: Recycling and reuse assessment into new composite materials using Fuzzy Boolean Nets. J. Clean.
Prod. 2014,66, 420–430. [CrossRef]
Materials 2021,14, 1399 15 of 16
13.
Vigneshwaran, S.; Sundarakannan, R.; John, K.; Johnson, R.D.J.; Prasath, K.A.; Ajith, S.; Arumugaprabu, V.; Uthayakumar,
M. Recent advancement in the natural fiber polymer composites: A comprehensive review. J. Clean. Prod.
2020
,277, 124109.
[CrossRef]
14.
Mohammed, L.; Ansari, M.N.M.; Pua, G.; Jawaid, M.; Islam, M.S. A Review on Natural Fiber Reinforced Polymer Composite and
Its Applications. Int. J. Polym. Sci. 2015,2015, 1–15. [CrossRef]
15.
Mahmud, S.; Hasan, K.M.F.; Jahid, A.; Mohiuddin, K.; Zhang, R.; Zhu, J. Comprehensive review on plant fiber-reinforced
polymeric biocomposites. J. Mater. Sci. 2021,56, 7231–7264. [CrossRef]
16.
Lotfi, A.; Li, H.; Dao, D.V.; Prusty, G. Natural fiber–reinforced composites: A review on material, manufacturing, and ma-
chinability. J. Thermoplast. Compos. Mater. 2021,34, 238–284. [CrossRef]
17.
Hernández-Díaz, D.; Villar-Ribera, R.; Espinach, F.X.; Julián, F.; Hernández-Abad, V.; Delgado-Aguilar, M. Impact properties and
water uptake behavior of old newspaper recycled fibers-reinforced polypropylene composites. Materials
2020
,13, 1079. [CrossRef]
18.
Oliver-Ortega, H.; Tarrés, Q.; Mutjé, P.; Delgado-Aguilar, M.; Méndez, J.A.; Espinach, F.X. Impact Strength and Water Uptake
Behavior of Bleached Kraft Softwood-Reinforced PLA Composites as Alternative to PP-Based Materials. Polymers
2020
,12, 2144.
[CrossRef]
19.
Thomason, J.L.; Fernandez, R.; Luis, J.J.F.i.M. A review of the impact performance of natural fiber thermoplastic composites.
Frontiers 2018,5, 60. [CrossRef]
20.
Rozman, H.D.; Lai, C.Y.; Ismail, H.; Ishak, Z.A.M. The effect of coupling agents on the mechanical and physical properties of oil
palm empty fruit bunch-polypropylene composites. Polym. Int. 2000,49, 1273–1278. [CrossRef]
21.
Feng, D.; Caulfield, D.F.; Sanadi, A.R. Effect of compatibilizer on the structure-property relationships of ke-naf-fiber/polypropylene
composites. Polym. Compos. 2001,22, 506–517. [CrossRef]
22.
Clemons, C.; Sanadi, A.R. Instrumented Impact Testing of Kenaf Fiber Reinforced Polypropylene Composites: Effects of
Temperature and Composition. J. Reinf. Plast. Compos. 2007,26, 1587–1602. [CrossRef]
23.
Marcovich, N.E.; Villar, M.A. Thermal and mechanical characterization of linear low-density polyethylene/wood flour composites.
J. Appl. Polym. Sci. 2003,90, 2775–2784. [CrossRef]
24.
Karamanlioglu, M.; Preziosi, R.; Robson, G.D. Abiotic and biotic environmental degradation of the bioplastic polymer poly(lactic
acid): A review. Polym. Degrad. Stab. 2017,137, 122–130. [CrossRef]
25.
Yu, L.; Dean, K.; Li, L. Polymer blends and composites from renewable resources. Prog. Polym. Sci.
2006
,31, 576–602. [CrossRef]
26.
Ramírez, M.G.L.; Satyanarayana, K.G.; Iwakiri, S.; De Muniz, G.B.; Tanobe, V.; Flores-Sahagun, T.S. Study of the properties of
biocomposites. Part I. Cassava starch-green coir fibers from Brazil. Carbohydr. Polym. 2011,86, 1712–1722. [CrossRef]
27.
Wróblewska-Krepsztul, J.; Rydzkowski, T.; Borowski, G.; Szczypi´nski, M.; Klepka, T.; Thakur, V.K. Recent progress in bi-
odegradable polymers and nanocomposite-based packaging materials for sustainable environment. Int. J. Polym. Anal. Charact.
2018,23, 383–395. [CrossRef]
28.
Nakajima, H.; Dijkstra, P.; Loos, K. The recent developments in biobased polymers toward general and engineering appli-cations:
Polymers that are upgraded from biodegradable polymers, analogous to petroleum-derived polymers, and newly developed.
Polymers 2017,9, 523.
29.
Sadasivuni, K.K.; Saha, P.; Adhikari, J.; Deshmukh, K.; Ahamed, M.B.; Cabibihan, J.J. Recent advances in mechanical prop-erties
of biopolymer composites: A review. Polym. Compos. 2020,41, 32–59. [CrossRef]
30.
Sampath, U.G.T.M.; Ching, Y.C.; Chuah, C.H.; Sabariah, J.J.; Lin, P.-C. Fabrication of Porous Materials from Natu-ral/Synthetic
Biopolymers and Their Composites. Materials 2016,9, 991. [CrossRef]
31.
Torres, F.G.; Rodriguez, S.; Saavedra, A.C. Green Composite Materials from Biopolymers Reinforced with Agroforestry Waste. J.
Polym. Environ. 2019,27, 2651–2673. [CrossRef]
32.
George, A.; Sanjay, M.; Srisuk, R.; Parameswaranpillai, J.; Siengchin, S. A comprehensive review on chemical properties and
applications of biopolymers and their composites. Int. J. Biol. Macromol. 2020,154, 329–338. [CrossRef]
33.
Lalit, R.; Mayank, P.; Ankur, K. Natural Fibers and Biopolymers Characterization: A Future Potential Composite Material. Stroj.
ˇ
Casopis J. Mech. Eng. 2018,68, 33–50. [CrossRef]
34. Corbière-Nicollier, T.; Gfeller Laban, B.; Lundquist, L.; Leterrier, Y.; Månson, J.A.E.; Jolliet, O. Life cycle assessment of bio-fibres
replacing glass fibres as reinforcement in plastics. Resour. Conserv. Recycl. 2001,33, 267–287. [CrossRef]
35.
Rebitzer, G.; Ekvall, T.; Frischknecht, R.; Hunkeler, D.; Norris, G.; Rydberg, T.; Schmidt, W.P.; Suh, S.; Weidema, B.P.; Pen-nington,
D.W. Life cycle assessment Part 1: Framework, goal and scope definition, inventory analysis, and applications. Environ. Int.
2004
,
30, 701–720. [CrossRef]
36.
Henton, D.; Gruber, P.; Lunt, J.; Randall, J. Polylactic Acid Technology. In Natural Fibers, Biopolymers, and Biocomposites; CRC Press:
Boca Raton, FL, USA, 2005; pp. 527–577.
37.
Weber, C.; Werner, H.; Deubel, T. A different view on Product Data Management/Product Life-Cycle Management and its future
potentials. J. Eng. Des. 2003,14, 447–464. [CrossRef]
38.
Buchert, T.; Neugebauer, S.; Schenker, S.; Lindow, K.; Stark, R. Multi-criteria Decision Making as a Tool for Sustainable Product
Development—Benefits and Obstacles. Procedia CIRP 2015,26, 70–75. [CrossRef]
39.
Ren, J.; Manzardo, A.; Mazzi, A.; Zuliani, F.; Scipioni, A. Prioritization of bioethanol production pathways in China based on life
cycle sustainability assessment and multicriteria decision-making. Int. J. Life Cycle Assess. 2015,20, 842–853. [CrossRef]
Materials 2021,14, 1399 16 of 16
40.
Zarte, M.; Pechmann, A.; Nunes, I.L. Decision support systems for sustainable manufacturing surrounding the product and
production life cycle—A literature review. J. Clean. Prod. 2019,219, 336–349. [CrossRef]
41.
Oliver-Ortega, H.; Julian, F.; Espinach, F.X.; Tarres, Q.; Ardanuy, M.; Mutjé, P. Research on the use of lignocellulosic fibers
reinforced bio-polyamide 11 with composites for automotive parts: Car door handle case study. J. Clean. Prod.
2019
,226, 64–73.
[CrossRef]
42.
Kagan, V.A.; McPherson, R.; Chung, J.S. An Advanced High Modulus (HMG) Short Glass-Fiber Reinforced Nylon 6: Part I—Role
and Kinetic of Fiber-Glass Reinforcements. J. Reinf. Plast. Compos. 2003,22, 1035–1044. [CrossRef]
43.
MatWeb.com Matweb—The Online Materials Information Resource. Available online: http://www.matweb.com/Search/
MaterialGroupSearch.aspx?GroupID=17 (accessed on 4 January 2021).
44.
Dorel, S.; Couturier, A.; Lacour, J.R.; Vandewalle, H.; Hautier, C.; Hug, F. Force-velocity relationship in cycling revisited: Benefit
of two-dimensional pedal forces analysis. Med. Sci. Sports Exerc. 2010,42, 1174–1183. [CrossRef]
45.
Bini, R.; Hume, P.; Croft, J.; Kilding, A. Pedal force effectiveness in cycling: A review of constraints and training effects. J. Sci.
Cycl. 2013,2, 11–24.
46.
Alvarez, G.; Vinyolas, J. A New Bicycle Pedal Design for On-Road Measurements of Cycling Forces. J. Appl. Biomech.
1996
,12,
130–142. [CrossRef]
47.
Mornieux, G.; Stapelfeldt, B.; Gollhofer, A.; Belli, A. Effects of Pedal Type and Pull-Up Action during Cycling. Int. J. Sports Med.
2008,29, 817–822. [CrossRef]
48. Turpin, N.A.; Watier, B. Cycling Biomechanics and Its Relationship to Performance. Appl. Sci. 2020,10, 4112. [CrossRef]
49.
Vogt, S.; Schumacher, Y.; Roecker, K.; Dickhuth, H.-H.; Schoberer, U.; Schmid, A.; Heinrich, L. Power Output during the Tour de
France. Int. J. Sports Med. 2007,28, 756–761. [CrossRef]
50.
Dorel, S.; Hautier, C.A.; Rambaud, O.; Rouffet, D.; Van Praagh, E.; Lacour, J.-R.; Bourdin, M. Torque and Power-Velocity
Relationships in Cycling: Relevance to Track Sprint Performance in World-Class Cyclists. Int. J. Sports Med.
2005
,26, 739–746.
[CrossRef] [PubMed]
51.
Vogt, S.; Roecker, K.; Schumacher, Y.; Pottgießer, T.; Dickhuth, H.-H.; Schmid, A.; Heinrich, L. Cadence-Power-Relationship
during Decisive Mountain Ascents at the Tour de France. Int. J. Sports Med. 2008,29, 244–250. [CrossRef]
52.
Vogt, S.; Schumacher, Y.O.; Blum, A.; Roecker, K.; Dickhuth, H.-H.; Schmid, A.; Heinrich, L. Cycling power output produced
during flat and mountain stages in the Giro d’Italia: A case study. J. Sports Sci. 2007,25, 1299–1305. [CrossRef] [PubMed]
53.
Mortazavian, S.; Fatemi, A. Fatigue behavior and modeling of short fiber reinforced polymer composites: A literature review. Int.
J. Fatigue 2015,70, 297–321. [CrossRef]
54.
Fu, S.-Y.; Lauke, B.; Mai, Y.-W. Chapter 12—Creep and fatigue of short fibre composites. In Science and Engineering of Short
Fibre-Reinforced Polymer Composites, 2nd ed.; Fu, S.-Y., Lauke, B., Mai, Y.-W., Eds.; Woodhead Publishing: Cambridge, UK, 2019; pp.
411–435.
55.
Mandell, J.F.; McGarry, F.J.; Huang, D.D.; Li, C.G. Some effects of matrix and interface properties on the fatigue of short
fiber-reinforced thermoplastics. Polym. Compos. 1983,4, 32–39. [CrossRef]
56.
McKeen, L.W. Chapter 8—Polyamides (Nylons). In Fatigue and Tribological Properties of Plastics and Elastomers, 2nd ed.; McKeen,
L.W., Ed.; William Andrew Publishing: Oxford, UK, 2010; pp. 175–228.
57.
Salazar, A.; Rico, A.; Rodriguez, J.; Escudero, J.S.; Seltzer, R.; Cutillas, F.M.D.L.E. Monotonic loading and fatigue response of a
bio-based polyamide PA11 and a petrol-based polyamide PA12 manufactured by selective laser sintering. Eur. Polym. J.
2014
,59,
36–45. [CrossRef]
58.
Madan, J.; Mani, M.; Lee, J.H.; Lyons, K.W. Energy performance evaluation and improvement of unit-manufacturing processes:
Injection molding case study. J. Clean. Prod. 2015,105, 157–170. [CrossRef]
59.
Gutowski, T.; Dahmus, J.; Thiriez, A. In Electrical energy requirements for manufacturing processes. In Proceedings of the 13th
CIRP International Conference on Life Cycle Engineering, Leuven, Belgium, 31 May–2 June 2006; pp. 623–628.
60.
Iwko, J.; Wroblewski, R.; Steller, R. Experimental study on energy consumption in the plasticizing unit of the injection molding
machine. Polimers 2018,63, 362–371. [CrossRef]
61.
Hesser, F.; Mihalic, M.; Paichl, B.J.; Wagner, M. Injection moulding unit process for LCA: Energy intensity of manufacturing
different materials at different scales. J. Reinf. Plast. Compos. 2016,36, 338–346. [CrossRef]
62.
Oliveux, G.; Dandy, L.O.; Leeke, G.A. Current status of recycling of fibre reinforced polymers: Review of technologies, reuse and
resulting properties. Prog. Mater. Sci. 2015,72, 61–99. [CrossRef]
63.
Kawada, J.; Kitou, M.; Mouri, M.; Kato, Y.; Katagiri, Y.; Matsushita, M.; Ario, T.; Kitou, O.; Usuki, A. Super impact absorbing
bio-alloys from inedible plants. Green Chem. 2017,19, 4503–4508. [CrossRef]
64.
Feraldi, R.; Sauer, B.; Cashman, S. Life Cycle Inventory of Plastic Fabrication Processes: Injection Molding and Thermoforming; Franklin
Associates: Baton Rouge, LA, USA, 2011; pp. 20–40.
65.
Joshi, S.V.; Drzal, L.T.; Mohanty, A.K.; Arora, S. Are natural fiber composites environmentally superior to glass fiber reinforced
composites? Compos. Part A Appl. Sci. Manuf. 2004,35, 371–376. [CrossRef]
66.
Vallero, D. Chapter 31—Controlling Air Pollution from Sources. In Fundamentals of Air Pollution, 5th ed.; Vallero, D., Ed.; Academic
Press: Boston, MC, USA, 2014; pp. 881–925.