1. Introduction
In recent years, the world population has exceeded 7.7 billion inhabitants, and it will probably rise to 8.6 billion by 2030 and 9.8 billion by 2050 [
1]. This exponential world demographic growth, accompanied by excessive industrialization, low diffusion, and the application of alternative technologies, causes an environmental crisis. Likewise, the consumption of polymers or plastics has increased rapidly in the last five decades; these petrochemicals have been partially replaced in specific circumstances and many natural materials are used such as wood, cotton, paper, wool, and leather, among others. The United Nations Environment Program (UNEP) tells us in its research that the magnitude of the generation of greenhouse gases (GHGs) linked to the production, use, and elimination of plastics from fossil fuels will increase by around 2.1 gigatons of carbon dioxide (Gt CO
2) by the year 2040 [
2]. Similarly, other sources calculate that these emissions from plastics were 1.7 Gt CO
2 in 2015 and will increase to about 6.5 Gt CO
2 by the year 2050, equivalent to 15% of the global carbon budget.
At the same time, Lozano et al. (2020) indicated that worldwide 33% of the total organic waste obtained is not managed correctly; for example, in Peru, only 1% of this waste is used, causing a disproportionate emission of GHG, highlighting methane and CO
2, contributing significantly to climate change [
3]. On the other hand, regarding industrialization in Peru, Muñoz et al. (2019) indicates the outstanding sector is the agro-industrial sector, as the sugar industry originates several organic wastes, which present a high content of lignin and cellulose, the latter being one of the compounds found in large quantities throughout the world. However, they are not used or valued [
4,
5,
6,
7]. Mendez-Matias et al. (2018) stressed that approximately 75% of each ton of sugarcane is organic solid waste, having a greater volume of bagasse generated in industrial and artisanal processes [
8]. The extensive use of expanded polystyrene (EPS) leads to the accumulation of plastic waste due to its non-degradability property in its natural state, which has generated severe environmental impacts (white pollution). One of the challenges in our society is the correct disposal of the waste produced by anthropogenic activities; as the production of synthetic polymers grows, the amount of plastic waste will also increase [
9,
10,
11]. Unfortunately, only a tiny fraction is recycled. It is an unavoidable dilemma due to the collection, cleaning, and separation processes; the materials obtained are not competitive with virgin materials. That is why there is an urgent need for more significant efforts to carry out monitoring in all periods, since these data on plastic waste, especially EPS, are of great importance to restore and improve the perspective of the global, regional, and local model, thereby optimizing prevention and collection strategies [
12,
13].
Given this increase in consumption and considering that toxic resources have been used in the manufacturing, use, and disposal process of EPS, some countries have regulated the manufacturing process. In contrast, others, such as the United States, have prohibited or restricted its use as food packaging [
14,
15,
16]. These measures have undoubtedly made it easier to reduce the amount of production; however, they do not solve the problem since, according to the data previously presented, except in Asia, the consumption of products destined for food packaging represents little more than 30% of total consumption, leaving pending the integral management of the remaining 70% [
17,
18]. In 1986, the United States Environmental Protection Agency (EPA) reported that the polystyrene manufacturing process was the fifth most significant source of hazardous waste, linking it to adverse health effects in humans, and in 2014 it was classified as a potential carcinogen [
19,
20]. Faced with this problem, the present research project was justified by proposing a new alternative in green chemistry to reduce the use of additives and thus generate a sustainable biomaterial [
21,
22,
23].
In this research, the use of mycelium was analyzed, referring to the associations that fungi generate in the roots for better absorption of water and nutrients as a consequence of the growth of filaments (hyphae) [
24,
25,
26]. Likewise, the use of waste as raw material or substrate, together with the biodegradability of the biomaterial at the end of its useful life and the extensive scale of materials that it could replace, guarantees better waste management in the future if it is applied efficiently [
27,
28]. The contribution of this research is made up of the physical and mechanical characterization with which a biomaterial composed of
Pleurotus ostreatus mycelium and sugarcane bagasse was obtained as a substitute for polystyrene foams, presenting itself as an alternative for the use of lignocellulosic waste from the agro-industrial sector, in such a way that it can serve future researchers generating harmony between ecosystems and the fundamental needs of human beings, contributing to the circular economy [
29].
Due to this, the objective of the research is to produce a composite biomaterial based on Pleurotus ostreatus mycelium and sugarcane bagasse as an alternative to polystyrene foams. For this purpose, the physical and mechanical parameters (density, water absorption, and texture) of the biomaterial were evaluated using physical–mechanical tests of the compound biomaterials of Pleurotus ostreatus mycelium and bagasse.
4. Discussion
This type of research, where microorganisms are immersed, is complex since there are factors involved in mycelial development, so constant and vigorous monitoring must be carried out [
41]. Even though the substrate was sterilized and the samples, including the controls, were kept under controlled conditions (darkness, temperature, humidity, and time), one of the samples presented contamination by external agents since the mycelium is susceptible and vulnerable in its development phase [
42]. To clarify the difference in performance in the samples, there are probable factors, such as, when injecting each sample, it can be deduced that there was not an adequate distribution of the mycelium seeds. Adding to the above, Elsacker et al. (2020) emphasize that in a large percentage of laboratories, there is a tendency to work with microorganisms such as bacteria and fungi, among others, which is why the probability of contamination of the substrate or mycelium, as well as the equipment, continues to exist during the sowing phase. Instruments are in an aseptic condition [
43]. The slightest change in any of the parameters can trigger a substantial variation in the development and homogeneity of the colonization [
44] and the manipulation of the sowing within the substrate, evidencing how complex the process is. Work with living organisms depends on controlled conditions to develop biomaterials based on mycelial growth [
45]. After all these considerations, it was possible to elaborate on the biomaterial composed of
Pleurotus ostreatus mycelium and sugarcane bagasse in question; the procedure is written in the Materials and Methods. This biomaterial does not have its own standards. Therefore, it was compared with the data obtained from biomaterials reported in the literature and with standard values of expanded polystyrene.
Results obtained from the physical–mechanical tests of the biomaterial composed of
Pleurotus ostreatus mycelium and sugarcane bagasse were compared with previous investigations of other biomaterials and polystyrene foam, finding significant differences. The low density is considered necessary in competitiveness with synthetic foams; in our results, an average density of 127.86–131.19 kg/m
3 was obtained, which means that their density is low; that is, they are light. These values are relatively close compared to the compounds made from
Pleurotus ostreatus and
Trametes versicolor mycelium with cereal stubble and nut shells by Rodríguez (2018), which obtained a density of 149.37 kg/m
3 [
37]. Likewise, Ocegueda et al. (2021), in their bioplastics made with Pleurotus ostreatus mycelium in lignocellulosic residues of oak (
Quercus castanea Née) and corn cob (
Zea mays), the average density values varied from 96–198 kg/m
3 [
38]. Apples et al. (2019), in their mycelial compounds with
Trametes multicolor and
Pleurotus ostreatus in substrates such as straw, sawdust, and cotton, obtained average values of 100–390 kg/m
3 [
39]. On the other hand, Jones et al. (2020) mention that biomaterials containing forest residue substrates, such as sawdust, have a density ranging between 60 and 300 kg/m
3. In contrast, those that contain “filler” agro-industrial waste substrates, such as straw fibers, among others, have low densities of around 130 kg/m
3; this could be verified since, in our research, we used agro-industrial waste, and our values are within the range indicated by the authors [
40]. Supporting this statement, we have the work of Rey et al. (2018), who made biomaterials from
Pleurotus ostreatus and residues such as sugarcane bagasse and rice grass, having an average density of 132.7 kg/m
3. The value was more similar to our result, and the authors highlight that the development of this type of biomaterial based on fungi for different applications is no longer an insubstantial issue and that it represents a high degree of originality [
30]. Likewise, Susel et al. (2021), in their bioplastics made with
Ganoderma lucidum and walnut shell residues and sawdust, obtained a density of 169 kg/m
3, indicating that they can be used in the non-structural construction field and recommending further analysis since these types of compounds are new and innovative [
41]. However, compared with the standard values of EPS, they present intervals that oscillate from 10–50 kg/m
3, a much lower range than the one obtained in this investigation. Despite this, the authors affirm that these biomaterials can be used as an alternative packaging material to traditional polystyrene foams for packaging different items or food, where their combination of low density and low cost gives a competitive advantage and, even though production is still limited, the production process is improving rapidly.
According to Pelletier et al. (2019), compounds based on mycelial growth can show variation even if the same type of fiber is used since it is directly proportional to the expansion of the mycelium’s tissue within the substrate, with more excellent moisture absorption in those that contain intertwined fibers, facilitating the propagation of water in the biomaterial [
46]. In our results, the percentage of water absorption was 23.55% for sample M1, 11.79% for sample M2, and 15.35% for sample M3, presenting M2 as having the best behavior. That is, it has a lower absorption. This percentage obtained is relatively low compared to the results by Rodríguez (2018), who found an absorption of 15%; they mention that this water absorption capacity of mycelium-based materials generates tremendous interest since they can be superabsorbent [
37]. Similarly, Apples et al. (2019) obtained a result of around 11.63%; this result is similar to ours, showing the homogeneity in the degree of colonization, as well as that the thickness of the fungal skin and the type of substrate influence the rigidity and the water resistance of biomaterials [
39].
On the other hand, Ocegueda Vega (2021) obtained a high degree of water absorption, between 33.66 and 40.2%, in their bioplastics. The author indicates that instead of seeing their high absorption capacity as a disadvantage, it can be leveraged in different areas [
38]. Checking these data, they were verified with the hypothesis proposed by Jones et al. (2020), which indicates that the absorption percentage of biomaterials made with forest residues varies from 30–43%, while that of those that include only agro-industrial residues is much lower with a range of 10–26%. This could also be verified with our data [
40]. Likewise, Rodríguez, Sarache, and Orrego (2014) mention that the percentage of water absorption of these compounds can directly alter the physical tests since both the substrates and the mycelium absorb a significant amount of water [
47]. Adding to the above, one of the drawbacks of the materials made from mycelium is its moisture absorption since it is higher compared to the standard values of expanded polystyrene (0.03–9% by weight) and can be a possible difficulty if it is applied within the construction sector (roofs, walls, among others) because it would cause leaks. The limitation in the volume of water absorption of these biomaterials increases their resistance to degradation when exposed to environmental conditions such as humidity, sunlight, and temperature variation, preserving their mechanical properties and dimensional stability [
48].
In the texture test, results of hardness, elasticity, and resilience were obtained. Samples M1, M2, and M3 obtained values of 0.538, 0.682, and 0.68 MPa, respectively, for elasticity. It was observed that the maximum stress in the fibers was recorded for sample M3, showing a difference between samples M1 and M3, the latter results being more significant. In research conducted by Appels et al. (2019), they subjected their samples to hot, cold, and unpressed processes, and the heat-pressed samples had a higher elastic modulus than the cold-pressed and non-pressed ones, obtaining a modulus of 0.24 MPa [
39]. Likewise, Susel et al. (2021) obtained a value of 0.392 MPa, concluding that the material has a high compressive strength and stressing that these compounds depend on the type of waste used as a substrate for the mycelium [
41]. Likewise, Jones et al. (2020) obtained average values of 1.43 M/Pa, indicating that the material can be used in applications where the support of high flexural loads is not demanded and recommending that an additional improvement of mycelium materials to promote colonization in the central part of the substrate is needed [
40]. Adding to the above, the authors in the literature mention that this characteristic can be affected by the applied techniques, such as pressing, since heat pressing can substantially increase tensile strength. Compared with expanded polystyrene, materials have registered values from 1.24–3.45 MPa. Therefore, density and flexural strength have a directly proportional relationship; conversely, biomaterials are consistent and firm but brittle. The resilience depends on the deviator stress for the lowest density; for higher density, this effect is very slight, increasing as the density of the material increases [
49]. Samples M1, M2, and M3 achieved values of 0.163, 0.209, and 0.238 J/m
3, respectively, about the same as those mentioned above; as emphasized, density influences mechanical properties. According to the literature, the mycelium’s composition, morphology, and physical–mechanical performance are influenced by substrate content, incubation conditions, and manufacturing processes [
50].
On the other hand, this type of biomaterial is still a pioneering field, and a standardized process to produce optimized material properties has yet to be identified. How to customize the types of substrates for certain fungal species still needs to be defined to maximize mycelium yield and optimize mechanical performance. It is of utmost importance to synthesize information from the scientific literature, patents, and experience to identify barriers and possibilities for effective implementation of mycelium-based compounds in industrial manufacturing, in the architectural interior design of apartments, or the packaging sector.