1. Introduction
Carbon fibers are often used as reinforcements in plastics due to their exceptional mechanical properties. However, the processes for producing these fibers alone have a high global warming potential (GWP) compared to other reinforcing fibers [
1,
2]. In particular, natural fibers have a much lower environmental footprint; however, they are used much less frequently in fiber-plastic composites. They are, unfortunately, not used as reinforcement when structural performance is crucial for several reasons: problems in fiber-resin interface, lower strength properties, moisture absorption, higher variance in performance, etc. [
3,
4,
5,
6]. Still, some natural fibers can achieve mechanical performances (stiffness) comparable to glass fibers [
7,
8].
Multiple studies have investigated the environmental impacts of fiber-reinforced plastics using life cycle analysis (LCA), which comprehensively quantifies potential environmental effects throughout a product’s life cycle—with contributions from raw material acquisition, manufacturing, distribution, and use, to end-of-life product disposal. This analysis accounts for various environmental consequences, health impacts, and risks related to resource usage [
9]. However, there is a lack of homogeneity in the application of the LCA method. The definition of methodological approaches retains an element of subjectivity, a factor seldom addressed when interpreting results [
10]. In addition, the life cycle stages covered (e.g., with or without the use phase or with or without consideration of the production and procurement of raw materials) varies enormously in the available publications [
11]. Duflou et al. [
12] presented an LCA study based on three impact measures (cumulative energy demand, greenhouse gas emissions, and environmental impact scores) for bio-based fiber-reinforced polymer composites as an alternative to metallic structures. Comparisons were made with, among other materials, glass fiber-reinforced polymers × aluminum and carbon fiber-reinforced polymers (CFRP) × steel. With respect to the first, the LCA analysis describes how aluminum structures might perform better since they produce slightly lighter structures and are easily recyclable. For the latter, the LCA suggests that steel and aluminum are eco-friendlier after long usage of the components: 132,000 km for steel automotive panels and 70,000 km for aluminum aircraft applications. Khorgade et al. [
13] focused on a GWP analysis covering the cradle-to-gate period of two bridges containing both steel and CFRP reinforcements. They have obtained a favorable
emission for the carbon counterpart given the fact that both the amount of concrete and reinforcement are to be used in the CFRP configuration. Mindermann et al. [
7] have produced a deep and interesting investigation of the sustainability and structural performance of natural fibers when used in coreless filament winding. Firstly, the authors provided an important set of fiber and resin properties, including composition, mechanical behavior, GWP, and price. They have selected 12 different fibers and evaluated them for both manufacturing aspects and structural behavior, using four-point bending tests. Results have shown that flax fibers performed better when compared to other bio-based fibers. For most LCA impact categories, in refs. [
7,
14,
15] it was also exhibited that the production of basalt fibers causes less environmental impact than the production of glass fibers. Considering the natural fibers alone, Beus et al. [
16] have covered several (plant-based) fiber types and different transport configurations—from the plantations to the industry—as well as cultivation procedures.
As suggested by Mindermann et al. [
7], it is worth noticing that the resin system plays a significant role in the composite ecological performance, mainly when natural fibers are taken into account. Niutta et al. [
17] have compared quasi-static mechanical properties of petroleum- and bio-based epoxy resins and found no significant difference between them, apart from the GWP, which gives the designer the freedom to choose a bio-based epoxy system not only for ecological but also for technical reasons. La Rosa et al. [
11] have introduced an LCA comparison study between a bio-based polymer composite and a conventional glass/epoxy one. Their results have shown that the major impact, in terms of environmental impact, is given by the resin system.
With regard to manufacturing processes capable of dealing with diverse fiber characteristics, tailored fiber placement (TFP) technology [
18,
19,
20,
21] can be cited. This textile manufacturing technique can deal with many fibrous materials by embroidery means. Little to no modifications are required when changing fiber types. Furthermore, by using TFP, the designer has a larger degree of freedom in terms of fiber placement: the rovings are stitched over a base material in predefined paths with high precision. Variations of properties due to the stitching process are evaluated by refs. [
22]. Almeida Jr. et al. [
23] have improved an already optimized component and results have shown that outstanding mechanical behavior can be obtained by TFP-made components even when compared with other high-performance composites. Poniecka et al. [
24] have used the process to evaluate the mechanical properties of different configurations of flax fibers—from UD to woven fabric—considering different TFP parameters. Their results have shown that strength values were higher in UD TFP samples when compared to conventional UD-reinforced composites. Furthermore, the obtained elastic modulus of flax fibers was larger than that of glass fibers.
Many studies have considered comparisons in terms of evaluating simple tests on coupons [
3,
4,
5,
7]. To the authors’ knowledge, little to none has been performed in terms of a component level. The objective of this work is to apply six different fibers, both natural and synthetic, as reinforcement in a component originally optimized for CFRP [
20,
23], and study manufacturing aspects and mechanical performance along with the GWP. The importance of comparing performances through a composite component (not coupons) lies in consideration of the manufacturing procedures, possible adaptations required for natural fibers and biogenic epoxy, and their influence on the component’s mechanical response. The fibers chosen are carbon, E-glass, basalt, flax, hemp, and jute. Furthermore, two resin systems were included in the experiment: a petroleum and a bio-based resin. The latter is 36% plant-based [
25], reducing its GWP. Firstly, basic experiments, such as linear density, density of the resins, and dry fiber tensile stiffness are performed to compare some of the mechanical properties of the composite constituents. Then, the topology-optimized component is manufactured and tested. Key results have shown that flax fibers have the potential to substitute glass fibers, for example, if one considers both mechanical properties and GWP. Moreover, basalt fibers have shown an outstanding performance. Furthermore, the resin nature plays little to no influence when carbon fibers are considered whereas it is the major aspect of GWP for plant-based natural fibers.
4. Conclusions
In this publication, experiments on a part level were conducted to compare the performance of different fiber+resin systems using specific stiffness and a global warming potential (GWP)-weighted specific stiffness, i.e., a value related to , as the main comparison parameters. The first parameter is well known, mainly in the aerospace industry, and carbon and glass fibers are the best performers. The second parameter is introduced in this study and has as an objective a proper trade-off between mechanical and ecological properties and was explained using the example of global warming potential (GWP), which is one aspect of an LCA.
The LCA is an instrument used for the comprehensive ecological evaluation of products, estimating their resulting environmental impact. The results of the LCA should provide an answer to the question “How much impact will have a product system have on the environment?”. As expected, when contemplating only the mechanical properties, synthetic fibers perform much better than natural ones. However, when analyzing the specific stiffness along with the GWP, natural fibers become a valuable choice. Still, as observed in key results herein provided, fibers alone do not present the full picture of the GWP in a composite part, mostly in plant-based natural fibers. It is almost indifferent to the nature of the resin when considering carbon fibers and, in the opposite direction, natural fiber-based composites’ GWP is more sensitive to resin’s than fiber’s emissions. Thus, the use of natural fibers with the aim of reducing emissions is counterproductive with petroleum-based resins. Glass fibers are in the middle ground, in which both fibers and resin emissions are close to each other. Flax fibers with the biogenic epoxy have performed well among the fibers+resin systems tested. This statement refers to the impact category ’global warming potential’, measured as the in fiber production, in correlation with the mechanical parameter—specific stiffness of the composite. In this study, the entire component, the brake booster, was used as the functional unit.
A comprehensive life cycle assessment according to the ISO 14040 [
40] standard includes a proper scoping of the product system, deciding which activities and processes belong to the life cycle of the product that is studied. Within a comprehensive LCA, following the aforementioned ISO standard [
40], a suitable framework is established for the product system. This framework includes decisions regarding the inclusion of activities and processes within the product’s life cycle for analysis. It also encompasses the incorporation of various impact assessment parameters like acidification potential (AP), eutrophication potential (EP), ozone depletion potential (ODP), land use (ecological footprint), cumulative energy demand (CED), human toxicity potential (HTP), and others. Additionally, considerations involve selecting geographical and temporal boundaries, the context of the study, relevant technology levels in the product system processes, and the study’s perspective—whether it should follow an assessment path to anticipate impacts of alternative choices or focus on attributing impacts linked to the studied activity.
These comprehensive studies are necessary in order to carry out an objective sustainability assessment of material systems and products. Due to the great complexity, which is mainly due to the difficulties in obtaining the relevant data, most publications, such as this one, contain partial aspects of a LCA. Future works will apply this framework so as to evaluate the stiffness of such components against other parameters of the LCA. Furthermore, the inclusion of a life-cycle costing evaluation, considering both synthetic and natural fibers, is also planned along with recycling aspects of both fibers and matrices.