Submitted Successfully!
To reward your contribution, here is a gift for you: A free trial for our video production service.
Thank you for your contribution! You can also upload a video entry or images related to this topic.
Version Summary Created by Modification Content Size Created at Operation
1 -- 8100 2022-12-07 04:10:27 |
2 format -4 word(s) 8096 2022-12-08 02:50:22 |

Video Upload Options

Do you have a full video?

Confirm

Are you sure to Delete?
Cite
If you have any further questions, please contact Encyclopedia Editorial Office.
Fernandez-Bunster, G.;  Pavez, P. Innovative Uses of Polyhydroxyalkanoates. Encyclopedia. Available online: https://encyclopedia.pub/entry/38156 (accessed on 15 June 2024).
Fernandez-Bunster G,  Pavez P. Innovative Uses of Polyhydroxyalkanoates. Encyclopedia. Available at: https://encyclopedia.pub/entry/38156. Accessed June 15, 2024.
Fernandez-Bunster, Guillermo, Pamela Pavez. "Innovative Uses of Polyhydroxyalkanoates" Encyclopedia, https://encyclopedia.pub/entry/38156 (accessed June 15, 2024).
Fernandez-Bunster, G., & Pavez, P. (2022, December 07). Innovative Uses of Polyhydroxyalkanoates. In Encyclopedia. https://encyclopedia.pub/entry/38156
Fernandez-Bunster, Guillermo and Pamela Pavez. "Innovative Uses of Polyhydroxyalkanoates." Encyclopedia. Web. 07 December, 2022.
Innovative Uses of Polyhydroxyalkanoates
Edit

Polyhydroxyalkanoate (PHA), a biodegradable polymer obtained from microorganisms and plants, have been widely used in biomedical applications and devices, such as sutures, cardiac valves, bone scaffold, and drug delivery of compounds with pharmaceutical interests, as well as in food packaging. The novel applications are based on the production and composition of the polymer, which can be modified by genetic engineering, a semi-synthetic approach, by changing feeding carbon sources and/or supplement addition, among others. The future of PHA is promising, and despite its production costs being higher than petroleum-based plastics, tools given by synthetic biology, bioinformatics, and machine learning, among others, have allowed for great production yields, monomer and polymer functionalization, stability, and versatility, a key feature to increase the uses of this interesting family of polymers.

biotechnology renewable polymers biodegradable polymers PHAs

1. Bacterial Accumulation and Bioremediation

One way to improve the production of biopolymers is by the use of cellular factories, which allow for the production and/or incorporation of monomers in the biopolymer that cannot be added via chemical synthesis. Additionally, cellular factories are less contaminant than using regular chemical synthesis, which requires several steps. As stated previously, monomer incorporation depends on the carbon source used by the producer, metabolic pathways involved in the conversion of carbon source to monomer, and PHA synthases and enzymes related to biopolymer production. In combination, monomers with specific side chains may be chemically modified to increase the functionality and possible applications of biopolymers [1].
To develop novel uses for PHA, understanding the mechanisms involved in PHA production allows researchers to synthesize and develop PHA-based material with desired properties from cell factories, able to produce high amounts of the biopolymer for industrial uses. Biotechnology, including synthetic and systems biology, as well as evolutionary engineering, can help to reduce time, labor, and costs for the production of polyester, aiming to compete with petroleum-based polymers. Historically, heterotrophic bacteria such as Cupriavidus spp. and Pseudomonas spp. have been used as the main PHA producer [2], while novel accumulators such as cyanobacteria and purple bacteria have been investigated for PHA producers due to their photosynthetic and nitrogen fixation abilities, avoiding the requirements of organic carbon and nitrogen sources [3]. Halophiles have also been used to reduce freshwater consumption and lower contamination risks by the high salt requirements.
Orellana-Saez et al. (2019) described Pseudomonas sp. MPC bacterial strain, isolated from Antarctica, as able to grow from sugars, ethylene glycol, and even toxic aromatic compounds, such as toluene, phenol, and chloro-compounds, to accumulate PHA, as well as 5-carbon compounds, such as xylose and arabinose. In bioremediation conditions, the strain may transform phenol to catechol and also degrade benzene, toluene, and styrene, a common material started used in industry. The strain synthesizes a combination of scl-co-mcl copolymers under glucose, while in xylose and arabinose, only mcl is obtained [4].
P. chlororaphis subsp. aurantiaca produced mcl-PHA from crude glycerol [5] from biodiesel production, having physical-chemical properties that render their high potential for use in the development of wound management materials. The polymer’s low crystallinity and hydrophobicity allow its use for the preparation of flexible and elastic films resistant to water, confirming the potential applicability of these materials for wound dressing applications [6].
One particularity of using PHA accumulators is that they can do two things simultaneously, as demonstrated by Papa et al. (2020), which established a mixed microbial culture as biorefinery to produce biomethane (CH4) and PHA simultaneously, aiming to valorize the organic compounds found on municipal solid waste (Organic Fraction of Municipal Solid Waste (OFMSW)) [7][8].
PHAs may be used as a carbon source for post-denitrification and micropollutant co-metabolism. In fact, PHB and PHV are the most common biopolymer used for the removal of phosphorus, chlorinated hydrocarbons, and micropollutants; more specifically, PHB is used as an electron donor source for in situ bioremediation [9]. Santorio et al. (2019) focused on the evaluation of the PHA’s potential use as an endogenous carbon source for denitrification [10], which supports the hypothesis that the lower the PHA concentration within the cells, the lower its use for denitrification, as the biomass prefers to store it as a carbon source [10].
Levett et al. (2019) described that PHA might be accumulated by bacterial strains during enhanced biological phosphorus removal (EBPR), in which, in an anaerobic phase, carbon-based acids within the wastewater, such as volatile fatty acids (VFA), are assimilated by the microorganisms and stored as PHA by phosphate accumulating organisms. In the following step, under oxygen conditions but carbon starvation, the biopolymer is used as a carbon and energy source for cell growth and to uptake and store phosphates and glycogen. The research group additionally tested drug removal, such as benzotriazole, 5-methyl-1H-benzotriazole, carbamazepine, ketoprofen and diclofenac, and ibuprofen, among others. For example, under different conditions, such as low phosphorus concentrations, ibuprofen was removed faster than higher phosphorus concentrations, but that degradation would depend on the bacterial composition [11]. Also, worth to mention that bacterial strains in biofilms may be grown on plastic carriers that are suspended in the system, which require biodegradation [12].
Amino acids and vitamins on the diet of the PHA producer Alcaligenes sp. NCIM 5085, using different carbon sources, such as sugar cane molasses, fructose, and wheat bran, affects the properties of the PHB: a different PHB was obtained, characterized by high molecular weight and crystallinity, with higher thermal stability than regular PHB. Sugar cane molasses with methionine supplementation increased the PHB maximum yield, because amino acid biosynthesis requires more energy (ATP) than other amino acids [13].
Natural PHA-producing organisms accumulate PHA as granules surrounded by lipids and proteins [1][14], as well as non-native recombinant producers. But, heterologous hosts do not necessarily use the same metabolic regulation as natural producers, making them possible better for large-scale production.
PHA production pathways, such as the β-oxidation pathway, may be diverted into PHA production via modifications on enzymes, such as enoyl-CoA hydratases (PhaJ) [15], FadB homologs (YfcX, PaaG, PaaF, and YdbU), among others [1]. A known example is the work of Taguchi et al., who produced poly(lactide-co-3- hydroxybutyrate) from non-related carbon sources. Specifically, the group added a synthetic metabolic pathway to transform pyruvate to lactate and then to lactyl-CoA, a substrate able to be used by engineered PHA synthases to copolymerize with 3HB monomers [16]. In terms of evolutionary engineering, research is usually based on the main PHA synthase or PhaC enzymes, which catalyze the polymerization of hydroxyacyl monomers, such as PHB, PHV, or others, to produce PHA polymers. There are different PhaC enzymes, depending on their substrate. For example, PhaC from Ralstonia eutropha has specificity to scl-PHA monomers, while PHA synthases from Pseudomonas sp. have substrate specificities to mcl-PHA monomers [17]. Laboratory evolutionary techniques may be used to generate novel PHA synthases with increased affinity and/or substrate specificity [18].
Natural PHA synthases only may use 3-, 4-, 5-, and 6-hydroxyacyl-CoA groups as substrates. By evolutionary engineering, several studies were attempted successfully to use lactate as a monomer in a 3HB copolymer by evolving propionyl-CoA transferase (Pct) and the phaC [19][20].
To engineer a microbial host to obtain PHAs using cheap carbon sources crucial, such as sugarcane molasses and sucrose, among others, can be done by metabolic engineering on the natural hosts by adding the PHA-producing genes, such as acetyl-CoA acetyltransferase (PhaA), acetoacetyl-CoA reductase (PhaB), and PHA synthase (PhaC) using acetyl-CoA as the starting metabolite on a heterologous host, by evolutionary engineering, among others (Jae Park, 2015). Sohn et al. developed a recombinant E. coli that use sucrose as a carbon source that produces 3HB and P(3HB-co-Lactic Acid) by the expression of the sacC gene, encoding for secreted β-fructofuranosidase that mediates sucrose hydrolysis into glucose and fructose [19].
Genetic engineering and directed evolution have based their efforts on class I and class II PHA synthases due to their being formed as a single subunit, while those of class III and class IV are multisubunit synthases. While some PHA synthases are well characterized, allowing for pinpoint modifications, a great number of PHA synthases do not possess a structural model for directed mutagenesis to improve activity, substrate specificity, and stability of these enzymes, requiring more “irrational approaches” [21].
Other molecular techniques to improve PHA synthesis are given by synthetic biology, fiving tools such as ribosome-binding site (RBS) optimization, promoter/repressor engineering, chromosomal integration, cell morphology engineering [22], and cell growth behavior re-programming, among others. The gene-editing tool CRISPR/Cas9 has been demonstrated to be an excellent tool for regulating PHA metabolic fluxes and PHA pathway optimization. Synthetic biology methods and genome-editing tools are the present and future of PHA production, which will allow people to obtain tailor-made biopolymers, decreasing production costs. The up-scaling processes to obtain higher amounts of PHA have been difficult to overcome in the past. Molecular approaches, such as RBS optimization, promoter/repressor optimization, gene deletion, or expression-weakening methods, have been developed in non-model organisms [23]. For instance, different PHA may be obtained by weakening the beta-oxidation cycle in Pseudomonas putida and Pseudomonas entomophila [24]. Other strategies include the downregulation of branch products, controlling oxygen availability, regulation of NADH/NAD+ ratios, increasing oxygen availability, and regulation of the PHA molecular weight and granules, forming larger PHA granules and regulating PHA molecular weight also help to enhance PHA production.
Enzyme evolution applied to PHA production has been considered effective in altering enzymatic function and/or carbon source flexibility. Despite natural evolution having allowed people to find novel bacterial strains able to accumulate PHA for survival as carbon source storage, enzymes are not necessarily adequate for industrial uses. Changes in carbon source, stress resistance, pH, and temperature, among others, may be currently modified and tailored for the required reactor. Because of this, the concept of “evolutionary engineering” appeared, currently named “directed evolution” [25], by gradually changing carbon source concentrations and growth conditions, aiming to adapt the bacterial strain to “harsh” conditions. This approach may be combined with site-specific mutagenesis but requires structural information to select an adequate site for the mutation. Taguchi et al. (2004) explain that also an “irrational” directed evolution approach can be used by random mutagenesis with selection and/or screening, which may generate the desired change or other non-planned features, generating novel biological functions by molecular evolutionary mechanisms [21].
Random mutagenesis is considered a directed evolution strategy that aims to introduce random (hence the name) point mutations into the genome. The type of mutagenesis may be divided into five categories: transitions (substitution of a purine nucleotide for another or a pyrimidine for another one), transversions (substitution of a purine for a pyrimidine or vice versa), deletions (removal of one or more nucleotides), insertions (addition of one or more nucleotides) and inversions) and inversions (a full 180° rotation of a DNA segment) [26]. These types of mutations may be produced by treating the bacteria or its nucleic acids with chemical mutagens [27], by error-prone PCRs [28] and saturation mutagenesis, among others.
Evolution systems can be applied to all the enzymes involved in polyhydroxyalkanoate biosynthesis. PhaC, the main synthase, for example, catalyzes the polymerization of 3-hydroxy-acid-CoAs, into PHA granules. The members of this protein family are categorized into three major classes in terms of the primary structures deduced from their DNA sequences and the substrate specificity of the enzymes [21]. In general terms, the effectiveness of PhaC is related to the characteristics of the generated biopolymer, such as molecular weight, monomer composition, and even the PHA cell content.
The concept of in vitro evolution of the PHA synthase starts with an “original” PHA synthase (or prototype). After random mutagenesis, a pool of mutants that goes under a high-throughput screening, such as fluorescence-activated cell sorting (FACS), looking for evolvants with increased activity, thermostability, and change of substrate specificity, among others, which may be used as an efficient production system of PHAs with desirable properties. Taguchi et al. used an error-prone DNA polymerase for mutagenesis during PCR and developed two assay methods to evaluate polymer accumulation in a recombinant E. coli strain, focusing on the mutant generation of the phaC synthase gene [21]. Using another approach, Rehm et al. used a single gene shuffling to the coding region of phaC to generate a completely shuffled DNA fragment with mutations [29]. Liu-Tzea et al. analyzed the catalytic domain of the PHB polymerase in Ralstonia pickettii T1, concluding that the Asn at position 285 (N285) participates in the cleavage of ester bonds in a study performed using evolutionary engineering, controlling its activity [30]. Other studies about evolutionary engineering on Ralstonia pickettii T1 can be found in several papers [31][32][33].
In Aeromonas caviae, a single aminoacid substitution on the PhaC synthase went under study, which is able to produce the polyhydroxyalkanoate copolymer [P(3HB-co-3HHx)], demonstrating that a change from asparagine 149 by serine or aspartate 171 by glycine (D171G) presented higher enzymatic activity. Combining evolutionary engineering and gen insertion in Ralstonia eutropha, the synergistic effect of both aminoacid changes allowed the use of longer 3HA units from octanoate and soybean oil as carbon sources. When fructose was used, the PHB synthesized had a higher molecular weight [34].
The structural function of PhaC will help in understanding accumulation and biopolymer composition, giving light to future protein engineering works to improve PHA yield and biopolymer [35]. Another way to cheapen the costs of PHA production is by using mixed microbial cultures (MMCs), due to the lack of sterilization required and simplifying the process control, as well as allowing the use of low-cost substrates, such as agro-forestry residues, industrial by-products and wastes [36].
The second-generation strategy does not rely solely on the addition of the PHA genes but also the selection of them: Carbon sources and substrate specificity (given by the phaC synthase gene) affect the chemical structure of the comonomer units, monomeric composition, and molecular weight. Between abnormal climate change, global warming, plastic waste accumulation, and other anthropogenic environmental issues, several metabolic engineering strategies may be used to develop efficient PHA-producers microbial host strains.
Foong et al., by synthetic biology, enhanced the PHA productivity of the marine photosynthetic purple nonsulfur bacterium Rhodovulum sulfidophilum, a weak halophile previously used as a platform for the production of biohydrogen, PHAs, and spider silk [37]. The problem with the bacterial strain was the low substrate affinity of PHA synthase, so by genome-wide mutagenesis induced by ethyl methanesulfonate together with ultraviolet irradiation dosages and by a single-cell mutant screening of high PHA-accumulating mutant R. sulfidophilum, they obtained a PHA producer with higher PHA yields [38]. They chose genome-wide mutagenesis considering the highly complex cellular metabolic processes within a versatile photosynthetic bacterium that are affected by light, oxygen, and carbon source availability [39][40]. The research demonstrated that a synthetic biology-based strain improvement approach, using genome-wide mutagenesis and high-throughput FACS for selection, simplified the mutant generation and screening processes for complex microorganisms, enhancing up to 1.7-fold higher volumetric PHA productivity and a faster accumulation speed.
Other studies related to the biosynthesis of PHBHHx have been done in engineered C. necator strains using CO2 as the sole carbon source. Different enzyme, carbon and nitrogen source combinations have shown that PHA composition may be regulated, highlighting that by using recombinant (R)-enoyl-CoA hydratase (PhaJ) with different substrate specificities [41].
A surprising heterologous host is Halomonas sp. TD01, a fully-genome sequenced halophile bacteria isolated from China, can be grown under high salt concentrations and pH, allowing an open fermentation without contamination [42]. Unfortunately, the bacterial strain did not possess a controllable repression system for gene expression has slowed down more applications for Halomonas sp. TD01. Specifically, propionic acid turns into propionyl-CoA, which can enter the PHBV synthesis pathway (from foreign bacteria) to form 3-hydroxyvalerate monomers. Gene editing tools, such as CRISPRi (clustered regularly interspaced short palindromic repeats interference) derived from the CRISPR/Cas9 system, provide an efficient method for targeted gene repression [43]. Basically, in the CRISPR system, the Cas9 protein (RNA-guided DNA endonuclease) binds to a small guide RNA (sgRNA), forming a protein-RNA complex that will bind to the targeted sequence [44]. Mutations in the Cas9 protein can produce a Cas9 protein with DNA-binding properties. This feature may be used to target specific DNA, block transcription, and interfere with RNA polymerases, among others [45], a process named CRISPRi. The molecular technique was used to regulate PHA production by repressing multiple genes or multiple targets on one gene [46]. Wei Tao et al. developed a CRISPRi system for the non-model organism Halomonas sp. TD01 was successfully constructed and enhanced PHB expression by the repression of the ftsZ, prpC, or gltA genes. ftsZ encodes for a bacterial fission ring formation protein for elongated cell morphology and longer cell sizes, prpC gene encodes for a 2-methylcitrate synthase that regulates the 3HV monomer ratio in PHBV copolymers. Finally, the repression of the gltA gene, which encodes for citrate synthase, shunted a greater proportion of acetyl-CoA from the tricarboxylic acid (TCA) cycle to PHB synthesis, being obtained 8% more biopolymer by the repression of the gltA gene [22]. Other gene editing tools, such as CRISPR-Cas12a, allow for the simultaneous insertion of genes into multiple specific loci of the heterologous host genome, helping to edit microbial genomes faster [47]. At the pace of current progress, it is feasible to think of more novel and efficient synthetic biology techniques that will be developed to edit, design, construct or regulate the PHA synthetic pathways in natural and non-natural production strains.
Another heterologous host with similar properties as Halomonas sp. TD01 is the H. bluephagenesis TD01 bacterial strain, which can grow rapidly, as well as under high salt concentrations and alkaline pH, making it suitable for cultivation during nonsterile, open, and fermentation processes [48]. By using the bacterial strain, the group deleted the chromosomal phaC gene by using CRISPR-Cas9 while also using a plasmid expressing the phaCJ gene cloned from Aeromonas hydrophila, obtaining PHB-HHx.

2. Packaging: More Than Food

Most PHA research is based on two main topics: Biomedical applications and food packaging, but biomaterial may also be used for feeding purposes. Feeding aquatic organisms with PHB was not deadly to animals [49], even positively affecting the growth rate, survival, and disease resistance of aquatic animals. PHB works as an additive as a supplier of short-chain length fatty acids to maintain an adequate microbiome in the gastrointestinal tract [50]. As in bacteria, PHB may be used as a carbon (energy) source by European sea bass [49], rainbow trout, and Chinese mitten crab [51], among others. Also, polyhydroxybutyrate is used as an antibiotic alternative against Vibrio campbelli in shrimps by stimulating the expression of heat-shock proteins 70 [52].
Wang et al. (2019) used PHB (1% to 4%) as diet supplementation, producing a feeding pellet to be used in large marine yellow croakers and sensitive weaned piglets [53]. Also, it appears to be species-specific because no difference was found in the growth of Nile tilapia [50][54].
Also, combinations with other biopolymers (named composites) may be obtained. PHB/cellulose composites have less brittleness and are stable, which may be used for food packaging [55]. Other examples are blends are polylactic acid (PLA), cellulose, and nanofibers, which can use PHB as a carrier system to develop compatibility between PLA and the nanofibers, improving the properties of the material, being used in packaging and construction material [56]. Other combinations, such as cellulose nanocrystals and PHB as bionanocomposites, improved UV barrier properties and reduction in water vapor permeation, with potential applications in the packaging [57], and the development of a PHB/cellulose cardboard with good mechanical properties that could be used in food packaging and the agriculture industry [58].
A nontoxic, stretchable, biocompatible and biodegradable polyurethane was prepared, characterized, and evaluated for biomedical applications based on L-lysine diisocyanate with poly(ethylene glycol) and polyhydroxyalkanoates (LPH) of different molar ratios were synthesized, demonstrating the viability of the LPH scaffolds for many biomedical applications [59].
Goonoo et al. (2017) developed novel blend films of anionic sulfated polysaccharides kappa-carrageenan (KCG) and fucoidan (FUC) derived from seaweeds with semi-crystalline PHB and PHBV and tested them in cells. Summarizing, mixtures presented higher surface hydrophilicity, higher water uptake, and immiscibility of polymer components, giving rise to an improved biological response of PHBV/KCG blends toward fibroblast growth [60].
The addition of silver nanoparticles (AgNPs) to generate materials with antimicrobial properties is promising for the food storage field [61], offering a strong antimicrobial activity against the food-borne pathogens Salmonella enterica and Listeria monocytogenes, which makes them potentially suitable for active coatings and packaging applications. Interestingly, the presence of the AgNPs did not impair the profile of biodegradation of the microbial polymer [62][63].
Requena et al. (2019) tested the antibacterial effect of PHBV films with oregano or clove essential oil, or their main compounds, carvacrol, and eugenol, respectively. The analysis was carried out in food matrices and in vitro tests for Escherichia coli and Listeria innocua [64].
ZnO nanoparticles can be used to enhance the properties of a PHB matrix, increasing the thermal stability and degree of crystallinity of the PHB matrix [65][66], as well as presenting antibacterial (Gram-positive and negative) properties, as well as a decrease in oxygen permeability, water vapor, and water uptake of the PHB host matrix, which may be used as antimicrobial plastic packaging [67]. Adding ZnO nanoparticles in a copolymer of PHBHHx allows for an increase in UV absorption, melting temperature, and thermal stability, making it suitable as a UV-blocking material or as packaging [68].
A blend of PHB/poly(butylene adipate-co-terephthalate; PBAT), together with the antimicrobial compounds of 1-allylhydantoin (AH) and perfluorooctyl acrylate (PFA), gave, as a result, a PHA-based membrane with ductility, stability, and hydrophobicity adequate for packaging applications [69]. Other mixtures, such as PLA/PHB [70], polyhydroxyalkanoates/cheese whey/gelatin (PHAs/CW/Gelatin) [71] and PHAs/nanokeratin [72] and PLA-based thermoplastic polyurethane (PLAPU) [73] also possess great features to be used as packaging material [64].
Active compounds may be volatile and may also affect the organoleptic properties of the food; for example, oils immobilized in silica changed the aroma of juice samples. For example, Figueroa-Lopez et al. (2020) used different concentrations of eugenol (C10H12O2)—commonly known as clove oil, recognized by its antibacterial properties against Gram-negative and positive strains [62]—and incorporated it into ultrathin fibers of PHBV to create antimicrobial monolayers, testing it against Staphylococcus aureus and Escherichia coli, with positive results [63]. Grape seeds lignin (1–5 wt%) positively affected the PHB/PHA films by improving their gas barrier properties, thermal stability, antioxidant activity, and biodegradability. As an end-product, the biodegraded polymer of PHA/PHB/lignin did not show toxicity [74]. Xavier et al. (2015) studied the incorporation of vanillin in PHB films for use against fungal strains, such as Aspergillus fumigatus, A. niger, A. ochraceus, and Penicillium viridicatum, and also against common pathogenic strains, like Escherichia coli, Salmonella typhimurium and Staphylococcus aureus [75]. Eugenol may also be added for its antifungal efficiency in the treatment of infections and/or food packaging [76].

3. Drug Delivery of Natural Compounds

The biopolymer storage technology, whose hydrophobicity may be configured, allows researchers to encapsulate organic compounds and tailor the biocapsule according to the compound’s properties. By having an engineered strain that produces a drug and encapsulation methods, for example, lycopene and PHB, respectively, encapsulation will be produced in vivo, increasing efficiency and lowering production costs. Additionally, other drugs may also be considered if their biosynthetic pathways are identified to be added to the E. coli strain. This type of methodology, commonly named “one-pot,” saves time and may avoid the use of organic solvents to extract the biosynthetic compound [77].
Heterologous gene expression in suitable hosts may be used for compound encapsulation. Fusing enzymes with PhaC allows the production of PHA granules with active enzymes on the surface, yielding various applications in scouring, bioseparation, imaging, and biomedical applications [78]. Former immobilization methods, such as cross-linking and encapsulation, require several steps that could negatively affect enzyme activity [79]. Tan et al. (2019) combined this methodology to add the genes for a tyrosinase (from Verrucomicrobium spinosum—TyrV) and immobilized it on the surface of PHA granules (also by the addition of the phaC synthase gene), where the resulting PHA-TyrVs nano-granules demonstrated L-DOPA (3,4-dihydroxyphenyl-L-alanine), a promising drug for Parkinson’s disease [80], forming monophenolase activity, and improving L-DOPA production [78][79][81][82]. The approach has been used before for the immobilization of polygalacturonate lyase (PGL), beta-galactosidase (LacZ) [29], N-acetylneuraminic acid aldolase (NanA) [83], immunoglobulin G (IgG)-binding domain (ZZ) [79], and mycobacterial antigens [84], among others.
Wong et al. (2020) developed a novel technology to use bioengineered PHA particles on engineered bacteria for protein immobilization by adding functional proteins by the SpyTag/SpyCatcher technology of protein ligation. This methodology relies on the production of PHA spheres with a specific domain described as the SpyCatcher domain and synthesizing a SpyTagged target protein that may be ligated to the PHA itself [85]. This strategy, according to the authors, is proposed as a versatile toolbox for PHA sphere functionalization with biomedical and industrial applications [86].
Levett et al. (2019) used it to deliver dicyandiamide (DCD) in PHBV pellets, a heat-sensitive stabilizer for nitrogen fertilizers, aiming to use it in tropical agriculture, characterized by high temperatures and fast microbial degradation [11]. Nitrogen fertilizers are described as very inefficient, and more than half of the fertilizer is lost in the environment and in terms of ammonia and urea volatilization and microbial transformations [87], so nitrification inhibitors, such as DCD, may help to decrease nitrogen losses and, simultaneously, increase plants’ nitrogen uptake [11]. The research group stated that PHAs suffer enzyme-catalyzed erosion at their surfaces as the degradation process in soil [88]. The main idea to use PHA to encapsulate hydrophobic molecules (i.e., compounds that repel water) is explained because biodegradable biopolymers such as PHA allow a controlled release of the encapsulated compound (such as the natural compounds carotene, morin, and the anti-cancer compound curcumin) by monitoring the degradation of the polymer [78], such as beta-carotene in mcl-PHA [89].
Latos-Brozio & Masek (2020) studied the degradation process of PHA biocomposites with natural antibiotic compounds. This is a very interesting idea, but PHA degradation depends on bacterial strains to degrade the polymer, so how biodegradation works when an antibiotic is added? Not only do microorganisms participate in the degradation, but also elevated temperatures and high humidity are adequate conditions for the two main mechanisms of degradation of polymeric materials: Hydrolytic degradation (a chemical-based process that breaks bonds within the polymer) and the biological-based enzymatic degradation by microorganisms [90].
Research groups used simultaneously the PHA bioaccumulation and drug encapsulation properties in the biopolymer-producing bacterial strains [91]: Liu et al. (2020) proposed and reported a methodology that allows the in vivo storage of hydrophobic products in/on biopolymer bodies in E. coli, using PHB to encapsulate lycopene, a red carotenoid hydrocarbon that can be found in red fruits and vegetables. After in vitro tests and in vivo characterization, they found that lycopene formed aggregation bodies in bacteria that did not produce PHB. The co-production of both lycopene and PHA titers simultaneously was positively correlated; for example, if a cell had high PHB content, it tended to have also a high lycopene content [77].
Modjinou et al. (2020) combined PHBHV with the monoterpene linalool extracted from spice plants, aiming to develop an antibacterial membrane, increasing the mechanical resistance flexibility and elongation at break. It is worth mentioning that linalool addition was by using a tetrafunctional cross-linking agent, and also the PHA-Linalool material presented anti-adherence properties against Escherichia coli and Staphylococcus aureus [92], while Latos-Brozio & Masek (2020) et al. studied PHA and PLA matrixes with the plant functional additives, (+)-catechin and polydatin, an anticancer/inflammatory/oxidant agent [93] to improve the biopolymeric material properties, obtaining a polyester with higher resistance to oxidation and degradation under the influence of UV radiation [90][94].
Improvement of PHAs polymer properties by adding functional groups could be a good approach to increase their biodegradability, economic value, and important applications in the medical field, as shown by Bhatia et al. (2019), who added ascorbic acid as an antioxidant to PHBV and obtained better mechanical properties and biodegradability [95].
PHA beads are being tested for industrial purposes, such as degrading dyes generated in the textile industry [96] or to support enzymes that synthesize molecules for food purposes, such as D-allulose, a potential sweetener [97]. Ran et al. (2017) reported that PHA bound to the enzyme PGL (Alkaline polygalacturonate lyase), one of the pectinolytic enzymes used for the bioscouring of cotton fibers, biodegumming, and biopulp production, resulting in a promising approach to immobilization of PGL in vivo, contributing to the wider commercialization of this environmentally friendly biocatalyst [83].
PHAs have been used to encapsulate bacteriophages [98], but no description can be found of bacterial immobilization. Gonzalez et al. (2020) went beyond this and encapsulated microorganisms within polyhydroxyalkanoate (PHA)-based microcapsules (MPs). At first, the group obtained a spherical PHA from a P. putida KT2440 strain by using a modified double emulsion solvent evaporation technique based on water/oil/water phase separation, testing a microencapsulation method on PHA by encapsulating the Bdellovibrio bacteriovorus bacterial strain [99].
Interestingly, double emulsion technology using mcl PHA may be used for microbial encapsulation with a controlled release while protecting the bacterial strain from environmental stress. This technology does not rely on a certain bacterial strain; instead, bacteria of biotechnological interest may be encapsulated for their use under stressful conditions or as antibiotics.

4. As a Biomaterial

Why use PHA? Companies are looking for materials that may replace metal parts with polymer-based materials. Polyhydroxyalkanoates may be prepared to have different morphologies and thermal/rheological properties. In terms of biodegradability, the material may be contaminated with other compounds, such as paraffin, in which, under the influence of an environment rich in enzymes, the compound may accelerate biodegradation, but under natural conditions, the contaminant slowed the biodegradation. Also, 3D printing increased the applications of biopolymers by allowing the preparation of specific pieces using the material without requiring molds. Additionally, they stated that the printing orientation of individual parts of the container might influence the properties of the material, individually for each region, in which every individual region had its degradation rate. One of the advantages of 3D printing is that researchers can create any complex shape.
Current technologies have been used to increase the applications of PHA: Gonzalez Aseujo et al. (2018) tested a polylactide/PHA material by using 3D printing and characterized its properties, including behavior during waste disposal [100].
Pop et al. (2020) used a PLA/PHA/Bamboo Fill filament for 3D printing and tested it for tensile, compression, and three-point bending strengths. The more interesting results related to PHA filament were that in pieces subjected to compression, the PLA/PHA/BambooFill materials were recommended in solid configuration, while the cylindrical architecture conferred better compressive strength compared to the standard architecture. In terms of impact resistance, the tensile strength of a 3D-printed sample will depend on the mass of the specimen for all materials [101].
The most recent research has focused on PHA and COVID. Why? Historically, the use of non-biodegradable plastics has increased from 245 million tonnes in 2008 to 368 million tonnes in 2019 [102], even estimated that nearly 1.6 million tonnes per day of plastic waste were produced due to the SARS-CoV-2 pandemic outbreak: Personal protective equipment (PPE), such as surgical facemasks and shield, latex or nitrile gloves, goggles, shoe covers, gowns, among others, are also considered as plastic waste [103].
One of the problems was the pollution produced by single-use face masks. By using 3D printing, Zgodavová et al. (2021) tested different biopolymers to test their biodegradability, being PHA selected by its environmental sustainability [104]. As PHA material, they used PHA BioWOOD Rosa 3D, a 100% natural biopolymer that decomposes without oxygen and water, with a wooden smell, unlikely other PHA biopolymers.
Other bio-composites based on polyhydroxyalkanoates (PHAs) and fibers of the aquatic plant Posidonia oceanica (PO) have been developed that can be suitable to manufacture items usable in marine environments, for example, in natural engineering interventions and represent an interesting valorization of the PO fibrous wastes accumulated in large amounts on coastal beaches [105].
Also, PHA-nanoclay blends were developed to improve the biopolymer properties, and developed nine nanobiocomposite materials, based on a linear PHB, poly(3-hydroxybutyrate)-co-poly(4-hydroxybutyrate; P3HB-co-P4HB); and nanoclays, aiming to customize copolymers to obtain semicrystalline copolymer structures designed to have tailored melting points, as well as controlling its brittleness, obtaining a PHA-nanoclay blend with better mechanical properties, also eliminating the characteristic odor of PHA [106].
Yu et al. (2019) proposed the synthesis of a novel fluorescent material by using highly efficient rare-earth, using PHA as a scaffold [107], as an alternative of Quantum Dots, described as the new-generation in fluorescent materials, which has the unwanted feature of releasing free ions and low solubility [108]. They used an engineered Halomonas bluephagenesis for PHA accumulation, and then N-acetyl-L-cysteine (NAL) was added by UV radiation and then combined with rare-earth material. As a result, they got a functionalized NAL-PHA material combined with the rare earth fluorescent material, with intense photoluminescence under UV excitation [48][109][110].
Most PHA research is focused on obtaining biopolymers from natural sources. Kageyama et al. (2021) went beyond and designed their biopolymer, namely poly(2-hydroxybutyrate-b-3-hydroxybutyrate [P(2HB-b-3HB)]), by using an engineered E. coli strain expressing a fused (chimeric) PHA synthase PhaCAR, as part of the novel strategy to use artificial PHA to improve the characteristics of the biopolymer by using unusual monomers that show distinct and unique properties [111]. The PHA synthase PhaC1PsSTQK [112] was discovered several years ago and incorporates different 2HA units, such as lactate and glycolate. Despite it being possible to obtain “artificial” PHA blocks, their biodegradability and cytotoxicity are under investigation but open an era in synthetic biology by being able to develop one’s “own” PHA synthase.

5. Applications of Electrospinning Technique on PHA

Electrospinning has garnered attention in recent years due to its potential for applications in various fields. Electrospun fibers have shown great applicability for novel materials in tissue engineering, wound healing, and bioactive molecules delivery, as well as sensor, filtration, composite reinforcement, and nanoelectronic applications. Electrospinning consists of a syringe through which a polymer solution is pumped, a high-voltage source, and a collector. The pendant drop of polymer solution held by surface tension forces at the tip of the syringe is electrified upon application of high voltage. As a result, electrostatic repulsion is established between like charges within the polymer solution, resulting in Coulomb forces due to the external field. When the strength of the electric field exceeds a threshold value that overcomes the surface tension of the polymer solution, a jet is produced from the pendant drop. The jet undergoes stretching and whipping while traveling toward the collector. The solvent evaporates during this process, and then a solid non-woven fibrous matrix is deposited on the collector. Several diverse polymeric materials have been electrospun, including synthetic and natural polymers. Among natural polymers, polyhydroxyalkanoates (PHAs) have useful properties such as biodegradability, thermoplasticity, biocompatibility, and non-toxicity [113].
Optimally post-processed electrospun fibers exhibited similar rigidity to conventional compression-molded PHA films but with enhanced elongation at break and toughness. Films made by electrospinning technique have, for instance, application interest in the design of barrier layers, adhesive interlayers, and coatings for fiber- and plastic-based food packaging materials [114], for example, the development and characterization of oxygen-scavenging films made of PHB containing palladium nanoparticles (PdNPs) prepared by electrospinning followed by annealing treatment at 160 °C. using hexadecyltrimethylammonium bromide (CTAB) as the dispersing aid. As a result, the PHB/PdNP nanocomposites containing CTAB offer significant potential as new active coating or interlayer systems for application in the design of novel active food packaging structures [115], while graphene-decorated silver nanoparticles (GAg) were incorporated into the fibers of poly-3 hydroxybutyrate-co-12 mol.% hydroxyhexanoate (P3HB-co-12 mol.% HHx), demonstrated significant reduction of S. aureus and E. coli as compared to solely to PHA. Therefore, the as-spun PHA/GAg nanocomposite may feasibly be efficient in the treatment of chronic wounds and sanitizing applications [116].
Future studies will focus on the application of PHB microfibers in several technological fields; for example, stearic acid-modified bilayers produced from the micro-nano-fibrous of SiO2 and PHBV composites showed very low water droplet sticking, which was possible to obtain superhydrophobic micro-nanofibers from PHBV-SiO2 [117].

6. Cosmetics

In cosmetic products, microplastics derived from toothpaste and cleansers, packaging, or face masks, have increased the environmental problem threatening whole ecosystems and human health, exacerbating the plastic problem to the extent that it is now one of the most serious global crises [118]. Additionally, not all petroleum-based plastics can be recycled, which solely only six types of plastics (polyethylene terephthalate, high-density polyethylene, polyvinyl chloride, low-density polyethylene, polypropylene, and polystyrene) may be partially recycled [119].
In biotechnology terms, the concept of accelerated aging is helpful in determining the lifespan or shelf-life of the product at an accelerated pace. Usually, research groups tend to study the rheological and mechanical properties of the biopolymer blends, but storage and shelf-time should also be considered for the market application [120]. In cosmetic products, also it must be considered physical and chemical stability under the country’s standards of safety in terms of storage [121] and/or transportation [120]. The challenge is to find adequate biopolymer cosmetics packaging that degrades even with residues of their content [121].
Compatibility tests must be considered before going to market to determine the interaction of the cosmetic formulation with the packaging in natural and shelf conditions. The ideal packaging should not react nor affect the cosmetic formulation and vice-versa, but also, physical conditions, such as appearance, color, and odor, should be taken into account. Also, depending on the material (PLA vs. PHA/PLA), paraffin (as a cosmetic compound) may accelerate or slow down degradation, among other statements. In general terms, the PLA/PHA blend demonstrated better compatibility with the cosmetic formulations [121].
PHA with starch blends has been used to prepare flexible films in beauty masks that can release starch (or other molecules) after wetting [122]. This strengthens the effort towards caring about raw materials and waste, positioning biotechnology as a promising science to impact the production of beauty ingredients and/or final products [123]. Renewable raw materials may protect the skin from contaminants, as well as modulate the skin’s microbiota, namely the ecological community of microorganisms that colonize body, adding to the ease of biodegradability and skin biocompatibility [124]. Also, it can be commercialized in a dry state without requiring preservatives [125]. For example, the structural, mechanical, antioxidant, and cytocompatibility properties of membranes prepared from the polyhydroxyalkanoate and arrowroot (Maranta arundinacea) starch powder blend demonstrate the enhanced functionality of arrowroot starch/polyester-based membranes for applications in the fields of drugs, food, cosmetics, and biomedical engineering packaging material [122][126].

7. As Sensor

PHB films may be used as a membrane to incorporate hemoglobin to boost the electron transfer rate of this protein, and other modifications, such as adding peroxidases and/or using pyrolytic graphite electrodes [127][128]. Phukon et al. (2014) used a hybrid nanocomposite combining 3-hydroxyvalerate (3HV), 5-hydroxydecenoate (5HDE), and 3-hydroxyoctadecenoate (3HODE) to be used as a biosensor was used for the quantitative detection of artemisinin in body fluids, combining gold nanoparticles and horse radish peroxidase [129].
Stojanovic et al. (2020) used polyhydroxyoctanoate (PHO) from a Pseudomonas putida KT2440 strain, prepared artificial saliva and simulated gastric fluid, aiming to evaluate it as a biosensor. In this particular example, they used pH as a reference because both liquids tested differ significantly in their pH values (Saliva 6.2–7.6; gastric fluid: 1–2). When the polymer was tested on saliva, it softened the material, while the immersion in gastric fluid diminished the resistance to mechanical force by the degradation of the polymer and double bonds rupture by the pH 1.2 of the fluid. Afterward, they tested the sensor applications by designing an inductor-capacitor structure composed of an interdigitated capacitor with five electrodes and a helically wound inductor. Then, gold was vapored to obtain the conductive structure at the top [127].
Organic and hydrogels, semisolid polymers based on three-dimensional networks, possess potential applications in organic electronics and photovoltaics: A hydrogel composed by poly[(R)-3-hydroxyundecanoate-co-(R)-3-hydroxy-10-undecenoate] (PHU10U—obtained from a Pseudomonas strain), with polyethylene glycol dithiol (PDT) as a photo-crosslinker [130] demonstrated good biocompatibility. In addition to the biomedical applications of organogels, such as drug and vaccine delivery matrices. They may also be used in environmental protection [131] and electronically active soft materials [130][132].
Carbon-based materials may be used as electrode materials in supercapacitors, defined as devices that store electrical energy in an electrical field, which are used in pieces of equipment that require fast charge/discharge cycles, such as vehicles and elevators, and energy storage, among others [133]. Common polymer precursors used usually collapse and aggregate during high-temperature treatment, resulting in low electrical conductivity and efficiency. Because of this, the carbon-based material may be improved post-heat treatment, but the compounds used to improve the pore structure may be corrosive, as well as only affecting the surfaces of the carbon [134]. A synergy was found between PHA and urea, which contributes to the incorporation of nitrogen within the carbon structure, producing a polymer with unique pore structures and higher porosity. This methodology is considered under the concept of in situ self-modification, in which urea modifies the PHA structure inside the bacterial strain, allowing the production of a biopolymer with high specific capacitance and energy density, excellent rate capability, and long cycling stability as supercapacitor electrode materials [133].
The self-modification strategy, which could be used in other areas of biotechnology, allows researchers to control PHA bacterial accumulation by regulating the composition of the cultivation media.
To improve the biopolymer’s properties, functional groups may be modified; for example, the functional groups of PHA (-OH (hydroxyl), -CO- (carbonyl), and -COO- (carboxyl)) generate gases, such as carbon mono- and dioxide and water, in the process called carbonization in high temperature. The carbonization process is used when complex carbonaceous substances are broken down into elemental carbon and chemical compounds (which also have carbon) by using heat. In this case, carbonization exfoliates the porous carbon, obtaining a larger surface area and highly porous structure, so when urea is added into the bacterial cell, it combines with PHA forming several nitrogen-containing functional groups, which release volatilized species during carbonization [135]. Specifically, the oxygen-containing functional groups interact with the nitrogen-based groups, thus incorporating nitrogen into the PHA matrix, producing a network with higher surface area and good conductivity, and as aimed, as an improvement in its performance as an electrochemical capacitor.

8. Other Uses

Other biocomposites, such as PHB/hydroxyapatite, were initially used as matrixes for bone implants and have been used for other biomedical purposes because of their good biocompatibility, osteoconductive and bioactivity [136], as well as high rigidity and low elasticity [137]. Chitin, found in shells of insects, lobsters, and shrimps, can interact with PHB to create a fully biodegradable composite [138] with potential applications in the agriculture and biomedical fields. Blends between PHB and natural fiber composites have better mechanical properties such as strength, stiffness, and others [57][139] and lowering production costs; for example, a blend between PHB/kenaf fiber and wood flour, enhancing tensile strength and elasticity [140], PHB and beech wood flour, obtaining a biopolymer with higher thermal stability, making them suitable for disposable articles [141], a film composite, based on PLA-PHB-limonene, with an adequate gas barrier, water resistance, and transparency for food packaging applications [142], among others. Also, biopolymers may be degraded in water, allowing their use in fresh fruit packaging or industrial products with short shelf life requirements [140][141][142].

8.1. As Flame Retardant

An interesting function of PHA is as a flame retardant [143]. A composite based on poly(3-hydroxybutyrate-co-3-hydroxyvalerate)/poly(butylene adipate-co-terephthalate; PHBV/PBAT), enhanced its flame retardancy properties, accompanied by good thermal and mechanical properties [144]. Additionally, combinations with aluminum phosphinate (AlPi), nanometric iron oxide, and antimony oxide has been introduced. PBAT degrades by enzymatic degradation within weeks and is used to improve the elongation/toughness of bio-blends, as well as the reduction in tensile strength and modulus, compared to the unmodified polymer [145]. The addition of AlPi (as a flame inhibitor in the gas phase) and the metal oxide nanofiller (as a stabilizer of intermediate structures containing oxygen) helps in the flame-retardancy mechanism. To obtain a composite with relatively good mechanical properties and with fire retardancy properties, Gallo et al. (2013) proposed a bi-layer laminate system based on biodegradable PHA, both of them based on PHBV/PBAT: One of them with the addition of aluminum diethylphosphinate flame retardant and nanosized antimony oxide, while the second layer had the kenaf fibers addition [146].

8.2. For Metabolic Pathways’ Analysis and Physiology

While not biomedical products per se, there is a need to understand how these polymers behave under physiological conditions in humans [147] and plants [148]. Little research has been made on the intracellular trafficking pathways of PHBHHx (3-hydroxybutyrate-co-3-hydroxyhexanoate) nanostructured materials. Biological studies can provide supportive information on the understanding of other spherical nanostructured materials as well. More recently, PHA as an electrospinning scaffold is also being investigated to produce sustainable in vitro models of biological barriers for investigating the physiopathological processes involved in the development of numerous diseases [147]. Sun et al. (2019) used Rab protein used as a marker to explore the intracellular trafficking mechanism of PHBHHx nanoparticles (NPs). When autophagy inhibitors and chemical drugs were packaged in PHBHHx and, used simultaneously, the volumes and weights of the tumors were significantly decreased. Additionally, NPs were internalized in cells mainly via clathrin endocytosis and caveolin endocytosis. Besides the classical pathways, they discovered two new pathways: the micropinocytosis early endosome (EEs)-micropinocytosis-lysosome pathway and the EEs-liposome-lysosome pathway. NPs were delivered to cells through endocytosis recycling vesicles and GLUT4 exocytosis vesicles. Similar to other nanoparticles, NPs also induced intracellular autophagy and were then degraded via endolysosomal pathways [147][148][149].
The overproduction of single-use plastic has generated an environmental crisis that has led people to look for compounds that degrade quickly, leaving no trace. In the environment, PHA polymer is degraded aerobically and anaerobically, using it as a carbon source. PHA depolymerases are produced by both bacteria and fungi. The degradation process depends on the characteristics of the PHA, such as crystallinity, size, thickness, molecular mass, and composition, but it also depends on temperature, pH, and humidity [150]. The time frame for biodegradation is critically important in defining the suitability of plastic for a particular end-of-life management technology or its likely fate in the environment. If the micro-organisms and, therefore, key enzymes involved in biodegradation are present, but the rate of degradation is so low that it does not differ significantly from non-degradable counterparts, then the limited biodegradability does not offer a benefit to the environment or the management of biodegradable waste. According to currently employed international standards, the proposed time frame for biodegradation in water environments is 56 days, and in soil, up to 2 years [151][152].
The key hydrolytic enzymes involved in the microbial degradation of PHA are depolymerases [151]. A variety of microorganisms have been identified that possess the enzymatic tools to degrade different types of PHAs, such as the genera Achromobacter, Nocardia, Variovorax, and Streptomyces. Streptomyces is the genus that produces the largest amount of PHA depolymerases. In combination with other polymers, it can degrade faster. For example, the use of tributyrin, dodecanol, lauric acid, and trilaurin increases degradation when used at 1% w/v. Much higher concentrations act as retardants.
Inside the body, the PHA polymer is broken down by the enzymatic action of proteins present in tissues and blood. Pancreatin, gastric juice, and bovine serum have been effective in degrading PHA microspheres. Pancreatin is composed of a mixture of esterases, lipases, amylases, and proteases. The active site of pancreatic lipase contains amino acid sequences, which are also present in the active site of PHB depolymerase [150].
It has been suggested that rapid PHBHHx degradation occurs in the amorphous region rather than in the crystalline region. At the same time, the in vivo hydrolysis of PHB was found to start from a random chain scission both in amorphous and crystalline regions of the polymer matrix. They also observed mild inflammatory effects of the implanted compound in the mice [153].
It is important that the degradation metabolites of the polymers, such as oligomers and monomers, are not harmful to surrounding tissue. PHB is mainly degraded under acidic conditions through acid hydrolysis of the ester bond in higher organisms. Oligomers produced by degradation have been shown to have positive effects on mouse fibroblast growth and are not detrimental to murine beta cells. The 3HB monomer is one of the three major ketone bodies that have regulatory effects on insulin secretion. 3HB has also been associated with high cellular calcium permeability by forming non-selective ion channels across the cell membrane. 3HB has a protective effect on dopaminergic neurodegeneration associated with increased mitochondrial respiration and ATP production [150].

8.3. As Cleaning Material

Organogels may be used as cleaning materials, particularly when a solvent-controlled delivery system is present to avoid substrate damage. PHB-based gels with green solvents were proposed to be a new cleaning system [154] by producing a compound that combines gels with other mechanically resistant materials to create a composite. Jia et al. (2020) developed an organogel based on poly(3-hydroxybutyrate) and γ-valerolactone for restoration, aiming to improve the removal process of varnish from a painting. For these purposes, the composite is formed by a PHA moiety encased, the core that contains the active solvent, in two external layers of nonwovens made of submicrometric fibers, either poly(vinyl alcohol) or polyamide. The composite material showed excellent cleaning properties by completely removing the varnish layer [155].

8.4. For Environmental Protection

By using PHA bionanoparticles, the immobilization of the lytic enzyme of a methanogen-integrated provirus, PeiR, inhibited an exceptionally broad range of different rumen methanogen strains in pure culture while significantly reducing methane production for several days, showing promising results that would decrease greenhouse gases [156].

References

  1. Lu, J.; Tappel, R.C.; Nomura, C.T. Mini-Review: Biosynthesis of Poly(hydroxyalkanoates). Polym. Rev. 2009, 49, 226–248. Available online: https://www.tandfonline.com/doi/abs/10.1080/15583720903048243 (accessed on 23 November 2022).
  2. Kourmentza, C.; Plácido, J.; Venetsaneas, N.; Burniol-Figols, A.; Varrone, C.; Gavala, H.N.; Reis, M.A.M. Recent Advances and Challenges towards Sustainable Polyhydroxyalkanoate (PHA) Production. Bioengineering 2017, 4, 55. Available online: https://pubmed.ncbi.nlm.nih.gov/28952534/ (accessed on 23 November 2022).
  3. Gradíssimo, D.G.; Xavier, L.P.; Santos, A.V. Cyanobacterial Polyhydroxyalkanoates: A Sustainable Alternative in Circular Economy. Molecules 2020, 25, 4331. Available online: https://pubmed.ncbi.nlm.nih.gov/32971731/ (accessed on 23 November 2022).
  4. Orellana-Saez, M.; Pacheco, N.; Costa, J.I.; Mendez, K.N.; Miossec, M.J.; Meneses, C.; Castro-Nallar, E.; Marcoleta, A.E.; Poblete-Castro, I. In-Depth Genomic and Phenotypic Characterization of the Antarctic Psychrotolerant Strain Pseudomonas sp. MPC6 Reveals Unique Metabolic Features, Plasticity, and Biotechnological Potential. Front. Microbiol. 2019, 10, 1154. Available online: https://pubmed.ncbi.nlm.nih.gov/31178851/ (accessed on 23 June 2022).
  5. Kumar, P.; Ray, S.; Patel, S.K.S.; Lee, J.K.; Kalia, V.C. Bioconversion of crude glycerol to polyhydroxyalkanoate by Bacillus thuringiensis under non-limiting nitrogen conditions. Int. J. Biol. Macromol. 2015, 78, 9–16.
  6. Pereira, J.R.; Araujo, D.; Marques, A.C.; Neves, L.A.; Grandfils, C.; Sevrin, C.; Alves, V.D.; Fortunato, E.; Reis, M.A.; Freitas, F. Demonstration of the adhesive properties of the medium-chain-length polyhydroxyalkanoate produced by Pseudomonas chlororaphis subsp. aurantiaca from glycerol. Int. J. Biol. Macromol. 2019, 122, 1144–1151. Available online: https://pubmed.ncbi.nlm.nih.gov/30219510/ (accessed on 15 October 2022).
  7. Papa, G.; Sciarria, T.P.; Carrara, A.; Scaglia, B.; D’Imporzano, G.; Adani, F. Implementing polyhydroxyalkanoates production to anaerobic digestion of organic fraction of municipal solid waste to diversify products and increase total energy recovery. Bioresour. Technol. 2020, 318, 124270. Available online: https://pubmed.ncbi.nlm.nih.gov/33099102/ (accessed on 24 June 2022).
  8. Molino, A.; Nanna, F.; Ding, Y.; Bikson, B.; Braccio, G. Biomethane production by anaerobic digestion of organic waste. Fuel 2013, 103, 1003–1009.
  9. Pierro, L.; Matturro, B.; Rossetti, S.; Sagliaschi, M.; Sucato, S.; Alesi, E.; Bartsch, E.; Arjmand, F.; Papini, M.P. Polyhydroxyalkanoate as a slow-release carbon source for in situ bioremediation of contaminated aquifers: From laboratory investigation to pilot-scale testing in the field. New Biotechnol. 2017, 37, 60–68.
  10. Santorio, S.; Fra-Vázquez, A.; Val del Rio, A.; Mosquera-Corral, A. Potential of endogenous PHA as electron donor for denitrification. Sci. Total. Environ. 2019, 695, 133747. Available online: https://pubmed.ncbi.nlm.nih.gov/31419685/ (accessed on 23 June 2022).
  11. Levett, I.; Pratt, S.; Donose, B.C.; Brackin, R.; Pratt, C.; Redding, M.; Laycock, B. Understanding the Mobilization of a Nitrification Inhibitor from Novel Slow Release Pellets, Fabricated through Extrusion Processing with PHBV Biopolymer. J. Agric. Food Chem. 2019, 67, 2449–2458. Available online: https://pubmed.ncbi.nlm.nih.gov/30724561/ (accessed on 23 June 2022).
  12. Torresi, E.; Tang, K.; Deng, J.; Sund, C.; Smets, B.F.; Christensson, M.; Andersen, H.R. Removal of micropollutants during biological phosphorus removal: Impact of redox conditions in MBBR. Sci. Total Environ. 2019, 663, 496–506. Available online: https://pubmed.ncbi.nlm.nih.gov/30716641/ (accessed on 23 June 2022).
  13. Tripathi, A.D.; Joshi, T.R.; Srivastava, S.K.; Darani, K.K.; Khade, S.; Srivastava, J. Effect of nutritional supplements on bio-plastics (PHB) production utilizing sugar refinery waste with potential application in food packaging. Prep. Biochem. Biotechnol. 2019, 49, 567–577. Available online: https://pubmed.ncbi.nlm.nih.gov/30929621/ (accessed on 23 June 2022).
  14. Uchino, K.; Saito, T.; Gebauer, B.; Jendrossek, D. Isolated poly(3-hydroxybutyrate) (PHB) granules are complex bacterial organelles catalyzing formation of PHB from acetyl coenzyme A (CoA) and degradation of PHB to acetyl-CoA. J. Bacteriol. 2007, 189, 8250–8256. Available online: https://pubmed.ncbi.nlm.nih.gov/17720797/ (accessed on 23 November 2022).
  15. Tsuge, T.; Fukui, T.; Matsusaki, H.; Taguchi, S.; Kobayashi, G.; Ishizaki, A.; Doi, Y. Molecular cloning of two (R)-specific enoyl-CoA hydratase genes from Pseudomonas aeruginosa and their use for polyhydroxyalkanoate synthesis. FEMS Microbiol. Lett. 2000, 184, 193–198. Available online: https://pubmed.ncbi.nlm.nih.gov/10713420/ (accessed on 23 November 2022).
  16. Taguchi, S.; Yamada, M.; Matsumoto, K.; Tajima, K.; Satoh, Y.; Munekata, M.; Ohno, K.; Kohda, K.; Shimamura, T.; Kambe, H.; et al. A microbial factory for lactate-based polyesters using a lactate-polymerizing enzyme. Proc. Natl. Acad. Sci. USA 2008, 105, 17323–17327. Available online: https://pubmed.ncbi.nlm.nih.gov/18978031/ (accessed on 23 November 2022).
  17. Nomura, C.; Taguchi, S. PHA synthase engineering toward superbiocatalysts for custom-made biopolymers. Appl. Microbiol. Biotechnol. 2007, 73, 969–979. Available online: https://pubmed.ncbi.nlm.nih.gov/17123079/ (accessed on 23 November 2022).
  18. Takase, K.; Taguchi, S.; Doi, Y. Enhanced synthesis of poly(3-hydroxybutyrate) in recombinant Escherichia coli by means of error-prone PCR mutagenesis, saturation mutagenesis, and in vitro recombination of the type II polyhydroxyalkanoate synthase gene. J. Biochem. 2003, 133, 139–145. Available online: https://pubmed.ncbi.nlm.nih.gov/12761209/ (accessed on 23 November 2022).
  19. Sohn, Y.J.; Kim, H.T.; Baritugo, K.-A.; Song, H.M.; Ryu, M.H.; Kang, K.H.; Jo, S.Y.; Kim, H.; Kim, Y.J.; Choi, J.-I.; et al. Biosynthesis of polyhydroxyalkanoates from sucrose by metabolically engineered Escherichia coli strains. Int. J. Biol. Macromol. 2020, 149, 593–599.
  20. Park, S.J.; Jang, Y.-A.; Lee, H.; Park, A.-R.; Yang, J.E.; Shin, J.; Oh, Y.H.; Song, B.K.; Jegal, J.; Lee, S.H.; et al. Metabolic engineering of Ralstonia eutropha for the biosynthesis of 2-hydroxyacid-containing polyhydroxyalkanoates. Metab. Eng. 2013, 20, 20–28.
  21. Taguchi, S.; Doi, Y. Evolution of Polyhydroxyalkanoate(PHA) Production System by“Enzyme Evolution”: Successful Case Studies of Directed Evolution. Macromol. Biosci. 2004, 4, 145–156. Available online: https://onlinelibrary.wiley.com/doi/full/10.1002/mabi.200300111 (accessed on 23 November 2022).
  22. Tao, W.; Lv, L.; Chen, G.-Q. Engineering Halomonas species TD01 for enhanced polyhydroxyalkanoates synthesis via CRISPRi. Microb. Cell Factories 2017, 16, 48. Available online: https://microbialcellfactories.biomedcentral.com/articles/10.1186/s12934-017-0655-3 (accessed on 23 November 2022).
  23. Zhang, X.; Lin, Y.; Wu, Q.; Wang, Y.; Chen, G.Q. Synthetic Biology and Genome-Editing Tools for Improving PHA Metabolic Engineering. Trends Biotechnol. 2020, 38, 689–700. Available online: https://pubmed.ncbi.nlm.nih.gov/31727372/ (accessed on 23 November 2022).
  24. Martínez-Tobón, D.I.; Waters, B.; Elias, A.L.; Sauvageau, D. Streamlined production, purification, and characterization of recombinant extracellular polyhydroxybutyrate depolymerases. Microbiologyopen 2020, 9, e1001. Available online: https://pubmed.ncbi.nlm.nih.gov/32087608/ (accessed on 23 November 2022).
  25. Tobin, M.B.; Gustafsson, C.; Huisman, G.W. Directed evolution: The “rational” basis for “irrational” design. Curr. Opin. Struct. Biol. 2000, 10, 421–427. Available online: https://pubmed.ncbi.nlm.nih.gov/10981629/ (accessed on 23 November 2022).
  26. Labrou, N.E. Random Mutagenesis Methods for In Vitro Directed Enzyme Evolution. Curr. Protein Pept. Sci. 2010, 11, 91–100. Available online: https://pubmed.ncbi.nlm.nih.gov/20201809/ (accessed on 23 November 2022).
  27. Jäckel, C.; Kast, P.; Hilvert, D. Protein Design by Directed Evolution. Annu. Rev. Biophys. 2008, 37, 153–173. Available online: https://www.annualreviews.org/doi/abs/10.1146/annurev.biophys.37.032807.125832 (accessed on 23 November 2022).
  28. Patrick, W.M.; Firth, A.E. Strategies and computational tools for improving randomized protein libraries. Biomol. Eng. 2005, 22, 105–112.
  29. Peters, V.; Rehm, B.H.A. In Vivo Enzyme Immobilization by Use of Engineered Polyhydroxyalkanoate Synthase. Appl. Environ. Microbiol. 2006, 72, 1777–1783. Available online: https://journals.asm.org/doi/10.1128/AEM.72.3.1777-1783.2006 (accessed on 9 October 2022).
  30. Tan, L.-T.; Hiraishi, T.; Sudesh, K.; Maeda, M. Effects of mutation at position 285 of Ralstonia pickettii T1 poly depolymerase on its activities. Appl. Microbiol. Biotechnol. 2014, 98, 7061–7068. Available online: https://pubmed.ncbi.nlm.nih.gov/24676749/ (accessed on 23 November 2022).
  31. Hiraishi, T.; Komiya, N.; Matsumoto, N.; Abe, H.; Fujita, M.; Maeda, M. Degradation and adsorption characteristics of PHB depolymerase as revealed by kinetics of mutant enzymes with amino acid substitution in substrate-binding domain. Biomacromolecules 2010, 11, 113–119. Available online: https://pubmed.ncbi.nlm.nih.gov/20058938/ (accessed on 23 November 2022).
  32. Hiraishi, T.; Hirahara, Y.; Doi, Y.; Maeda, M.; Taguchi, S. Effects of Mutations in the Substrate-Binding Domain of Poly (PHB) Depolymerase from Ralstonia pickettii T1 on PHB Degradation. Appl. Environ. Microbiol. 2006, 72, 7331–7338. Available online: https://pubmed.ncbi.nlm.nih.gov/16963553/ (accessed on 23 November 2022).
  33. Tan, L.-T.; Hiraishi, T.; Sudesh, K.; Maeda, M. Directed evolution of poly depolymerase using cell surface display system: Functional importance of asparagine at position 285. Appl. Microbiol. Biotechnol. 2012, 97, 4859–4871. Available online: https://pubmed.ncbi.nlm.nih.gov/22940802/ (accessed on 23 November 2022).
  34. Tsuge, T.; Watanabe, S.; Shimada, D.; Abe, H.; Doi, Y.; Taguchi, S. Combination of N149S and D171G mutations in Aeromonas caviae polyhydroxyalkanoate synthase and impact on polyhydroxyalkanoate biosynthesis. FEMS Microbiol. Lett. 2007, 277, 217–222. Available online: https://pubmed.ncbi.nlm.nih.gov/18031343/ (accessed on 23 November 2022).
  35. Chek, M.F.; Hiroe, A.; Hakoshima, T.; Sudesh, K.; Taguchi, S. PHA synthase (PhaC): Interpreting the functions of bioplastic-producing enzyme from a structural perspective. Appl. Microbiol. Biotechnol. 2019, 103, 1131–1141. Available online: https://pubmed.ncbi.nlm.nih.gov/30511262/ (accessed on 23 November 2022).
  36. Queirós, D.; Lemos, P.; Rossetti, S.; Serafim, L.S. Unveiling PHA-storing populations using molecular methods. Appl. Microbiol. Biotechnol. 2015, 99, 10433–10446. Available online: https://link.springer.com/article/10.1007/s00253-015-7010-6 (accessed on 23 November 2022).
  37. Foong, C.P.; Higuchi-Takeuchi, M.; Ohtawa, K.; Asai, T.; Liu, H.; Ozeki, Y.; Numata, K. Engineered Mutants of a Marine Photosynthetic Purple Nonsulfur Bacterium with Increased Volumetric Productivity of Polyhydroxyalkanoate Bioplastics. ACS Synth. Biol. 2022, 11, 909–920. Available online: https://pubs.acs.org/doi/full/10.1021/acssynbio.1c00537 (accessed on 18 February 2022).
  38. Chandrasekhar, K.; Jujjavarapu, S.E.; Kumar, P.; Kumar, G.; Chandrasai, P.D.; Kumar, E.M.; Chavali, M. Sources of Natural Polymers from Microorganisms with Green Nanoparticles. In Green Polymeric Nanocomposites; CRC Press: Boca Raton, FL, USA, 2020; pp. 103–132. Available online: https://www.taylorfrancis.com/chapters/edit/10.1201/9781351045155-5/sources-natural-polymers-microorganisms-green-nanoparticles-chandrasekhar-satya-eswari-jujjavarapu-prasun-kumar-gopalakrishnan-kumar-potla-durthi-chandrasai-enamala-manoj-kumar-murthy-chavali (accessed on 23 November 2022).
  39. Hädicke, O.; Grammel, H.; Klamt, S. Metabolic network modeling of redox balancing and biohydrogen production in purple nonsulfur bacteria. BMC Syst. Biol. 2011, 5, 150. Available online: https://pubmed.ncbi.nlm.nih.gov/21943387/ (accessed on 23 November 2022).
  40. Alsiyabi, A.; Immethun, C.M.; Saha, R. Modeling the Interplay between Photosynthesis, CO2 Fixation, and the Quinone Pool in a Purple Non-Sulfur Bacterium. Sci. Rep. 2019, 9, 12638. Available online: https://pubmed.ncbi.nlm.nih.gov/31477760/ (accessed on 23 November 2022).
  41. Tanaka, K.; Yoshida, K.; Orita, I.; Fukui, T. Biosynthesis of Poly(3-hydroxybutyrate- co-3-hydroxyhexanoate) from CO2 by a Recombinant Cupriavidusnecator. Bioengineering 2021, 8, 179. Available online: https://pubmed.ncbi.nlm.nih.gov/34821745/ (accessed on 23 November 2022).
  42. Tan, D.; Xue, Y.-S.; Aibaidula, G.; Chen, G.-Q. Unsterile and continuous production of polyhydroxybutyrate by Halomonas TD01. Bioresour. Technol. 2011, 102, 8130–8136.
  43. Barrangou, R.; Fremaux, C.; Deveau, H.; Richards, M.; Boyaval, P.; Moineau, S.; Romero, D.A.; Horvath, P. CRISPR provides acquired resistance against viruses in prokaryotes. Science 2007, 315, 1709–1712. Available online: https://www.science.org/doi/10.1126/science.1138140 (accessed on 23 November 2022).
  44. Cong, L.; Ran, F.A.; Cox, D.; Lin, S.; Barretto, R.; Habib, N.; Hsu, P.D.; Wu, X.; Jiang, W.; Marraffini, L.A.; et al. Multiplex genome engineering using CRISPR/Cas systems. Science 2013, 339, 819–823.
  45. Chen, G.Q. A microbial polyhydroxyalkanoates (PHA) based bio- and materials industry. Chem. Soc. Rev. 2009, 38, 2434–2446. Available online: https://pubs.rsc.org/en/content/articlehtml/2009/cs/b812677c (accessed on 23 November 2022).
  46. Lv, L.; Ren, Y.L.; Chen, J.C.; Wu, Q.; Chen, G.Q. Application of CRISPRi for prokaryotic metabolic engineering involving multiple genes, a case study: Controllable P(3HB-co-4HB) biosynthesis. Metab. Eng. 2015, 29, 160–168.
  47. Ao, X.; Yao, Y.; Li, T.; Yang, T.-T.; Dong, X.; Zheng, Z.-T.; Chen, G.-Q.; Wu, Q.; Guo, Y. A Multiplex Genome Editing Method for Escherichia coli Based on CRISPR-Cas12a. Front. Microbiol. 2018, 9, 2307. Available online: https://www.frontiersin.org/articles/10.3389/fmicb.2018.02307/full (accessed on 23 November 2022).
  48. Fu, X.-Z.; Tan, D.; Aibaidula, G.; Wu, Q.; Chen, J.-C.; Chen, G.-Q. Development of Halomonas TD01 as a host for open production of chemicals. Metab. Eng. 2014, 23, 78–91.
  49. Pakalapati, H.; Chang, C.-K.; Show, P.L.; Arumugasamy, S.K.; Lan, J.C.-W. Development of polyhydroxyalkanoates production from waste feedstocks and applications. J. Biosci. Bioeng. 2018, 126, 282–292. Available online: https://pubmed.ncbi.nlm.nih.gov/29803402/ (accessed on 21 June 2022).
  50. Thompson, C.L.; Wang, B.; Holmes, A.J. The immediate environment during postnatal development has long-term impact on gut community structure in pigs. ISME J. 2008, 2, 739–748. Available online: https://www.nature.com/articles/ismej200829 (accessed on 9 October 2022).
  51. Sui, L.; Ma, G.; Lu, W.; Deng, Y.; Bossier, P.; De Schryver, P. Effect of poly-β-hydroxybutyrate on growth, enzyme activity and intestinal microbial community of Chinese mitten crab, Eriocheir sinensis(Milne-Edwards) juveniles. Aquac. Res. 2015, 47, 3644–3652. Available online: https://onlinelibrary.wiley.com/doi/full/10.1111/are.12817 (accessed on 9 October 2022).
  52. Baruah, K.; Huy, T.T.; Norouzitallab, P.; Niu, Y.; Gupta, S.K.; De Schryver, P.; Bossier, P. Probing the protective mechanism of poly-ß-hydroxybutyrate against vibriosis by using gnotobiotic Artemia franciscana and Vibrio campbellii as host-pathogen model. Sci. Rep. 2015, 5, 9427. Available online: https://www.nature.com/articles/srep09427 (accessed on 9 October 2022).
  53. Wang, X.; Jiang, X.; Wu, F.; Ma, Y.; Che, X.; Chen, X.; Liu, P.; Zhang, W.; Ma, X.; Chen, G. Microbial Poly-3-Hydroxybutyrate (PHB) as a Feed Additive for Fishes and Piglets. Biotechnol. J. 2019, 14, e1900132. Available online: https://pubmed.ncbi.nlm.nih.gov/31119892/ (accessed on 23 June 2022).
  54. Situmorang, M.L.; De Schryver, P.; Dierckens, K.; Bossier, P. Effect of poly-β-hydroxybutyrate on growth and disease resistance of Nile tilapia Oreochromis niloticus juveniles. Veter.-Microbiol. 2015, 182, 44–49. Available online: https://pubmed.ncbi.nlm.nih.gov/26711027/ (accessed on 9 October 2022).
  55. Raza, Z.A.; Noor, S.; Khalil, S. Recent developments in the synthesis of poly(hydroxybutyrate) based biocomposites. Biotechnol. Prog. 2019, 35, e2855. Available online: https://pubmed.ncbi.nlm.nih.gov/31136087/ (accessed on 9 October 2022).
  56. Kiziltas, A.; Nazari, B.; Kiziltas, E.E.; Gardner, D.J.; Han, Y.; Rushing, T.S. Method to reinforce polylactic acid with cellulose nanofibers via a polyhydroxybutyrate carrier system. Carbohydr. Polym. 2016, 140, 393–399.
  57. Seoane, I.T.; Fortunati, E.; Puglia, D.; Cyras, V.P.; Manfredi, L.B. Development and characterization of bionanocomposites based on poly(3-hydroxybutyrate) and cellulose nanocrystals for packaging applications. Polym. Int. 2016, 65, 1046–1053. Available online: https://onlinelibrary.wiley.com/doi/full/10.1002/pi.5150 (accessed on 9 October 2022).
  58. Seoane, I.T.; Manfredi, L.B.; Cyras, V.P. Properties and Processing Relationship of Polyhydroxybutyrate and Cellulose Biocomposites. Procedia Mater. Sci. 2015, 8, 807–813.
  59. Wang, C.; Xie, J.; Xiao, X.; Chen, S.; Wang, Y. Development of Nontoxic Biodegradable Polyurethanes Based on Polyhydroxyalkanoate and L-lysine Diisocyanate with Improved Mechanical Properties as New Elastomers Scaffolds. Polymers 2019, 11, 1927. Available online: https://www.mdpi.com/2073-4360/11/12/1927/htm (accessed on 15 October 2022).
  60. Goonoo, N.; Bhaw-Luximon, A.; Passanha, P.; Esteves, S.; Schönherr, H.; Jhurry, D. Biomineralization potential and cellular response of PHB and PHBV blends with natural anionic polysaccharides. Mater. Sci. Eng. C 2017, 76, 13–24.
  61. Castro-Mayorga, J.L.; Freitas, F.; Reis, M.A.M.; Prieto, M.A.; Lagaron, J.M. Biosynthesis of silver nanoparticles and polyhydroxybutyrate nanocomposites of interest in antimicrobial applications. Int. J. Biol. Macromol. 2018, 108, 426–435. Available online: https://pubmed.ncbi.nlm.nih.gov/29217186/ (accessed on 20 June 2022).
  62. Kim, J.; Marshall, M.R.; Wei, C.-I. Antibacterial activity of some essential oil components against five foodborne pathogens. J. Agric. Food Chem. 1995, 43, 2839–2845. Available online: https://pubs.acs.org/doi/abs/10.1021/jf00059a013 (accessed on 9 October 2022).
  63. Figueroa-Lopez, K.J.; Cabedo, L.; Lagaron, J.M.; Torres-Giner, S. Development of Electrospun Poly(3-hydroxybutyrate-co-3-hydroxyvalerate) Monolayers Containing Eugenol and Their Application in Multilayer Antimicrobial Food Packaging. Front. Nutr. 2020, 7, 140. Available online: https://pubmed.ncbi.nlm.nih.gov/33015118/ (accessed on 24 June 2022).
  64. Requena, R.; Vargas, M.; Chiralt, A. Eugenol and carvacrol migration from PHBV films and antibacterial action in different food matrices. Food Chem. 2018, 277, 38–45. Available online: https://pubmed.ncbi.nlm.nih.gov/30502160/ (accessed on 21 June 2022).
  65. Díez-Pascual, A.M.; Díez-Vicente, A.L. Poly(3-hydroxybutyrate)/ZnO Bionanocomposites with Improved Mechanical, Barrier and Antibacterial Properties. Int. J. Mol. Sci. 2014, 15, 10950–10973. Available online: https://www.mdpi.com/1422-0067/15/6/10950/htm (accessed on 9 October 2022).
  66. Díez-Pascual, A.M.; Díez-Vicente, A.L. ZnO-Reinforced Poly(3-hydroxybutyrate-co-3-hydroxyvalerate) Bionanocomposites with Antimicrobial Function for Food Packaging. ACS Appl. Mater. Interfaces 2014, 6, 9822–9834. Available online: https://pubs.acs.org/doi/abs/10.1021/am502261e (accessed on 9 October 2022).
  67. Mallakpour, S.; Sirous, F.; Hussain, C.M. A journey to the world of fascinating ZnO nanocomposites made of chitosan, starch, cellulose, and other biopolymers: Progress in recent achievements in eco-friendly food packaging, biomedical, and water remediation technologies. Int. J. Biol. Macromol. 2020, 170, 701–716. Available online: https://pubmed.ncbi.nlm.nih.gov/33388319/ (accessed on 24 June 2022).
  68. Chandar, J.V.; Shanmugan, S.; Mutharasu, D.; A Azlan, A. Poly (3-hydroxybutyrate-co-15 mol% 3hydroxyhexanoate)/ZnO nanocomposites by solvent casting method: A study of optical, surface, and thermal properties. Mater. Res. Express 2017, 4, 015301. Available online: https://iopscience.iop.org/article/10.1088/2053-1591/4/1/015301 (accessed on 9 October 2022).
  69. In, X.; Fan, X.; Li, R.; Li, Z.; Ren, T.; Ren, X.; Huang, T.-S. Preparation and characterization of PHB/PBAT-based biodegradable antibacterial hydrophobic nanofibrous membranes. Polym. Adv. Technol. 2017, 29, 481–489. Available online: https://onlinelibrary.wiley.com/doi/full/10.1002/pat.4137 (accessed on 9 October 2022).
  70. Burgos, N.; Armentano, I.; Fortunati, E.; Dominici, F.; Luzi, F.; Fiori, S.; Cristofaro, F.; Visai, L.; Jiménez, A.; Kenny, J.M. Functional Properties of Plasticized Bio-Based Poly(Lactic Acid)_Poly(Hydroxybutyrate) (PLA_PHB) Films for Active Food Packaging. Food Bioprocess Technol. 2017, 10, 770–780. Available online: https://link.springer.com/article/10.1007/s11947-016-1846-3 (accessed on 9 October 2022).
  71. de Andrade, C.S.; Fonseca, G.G.; Mei, L.H.I.; Fakhouri, F.M. Development and characterization of multilayer films based on polyhydroxyalkanoates and hydrocolloids. J. Appl. Polym. Sci. 2016, 134, 44458. Available online: https://onlinelibrary.wiley.com/doi/full/10.1002/app.44458 (accessed on 9 October 2022).
  72. Fabra, M.J.; Pardo, P.; Martínez-Sanz, M.; Lopez-Rubio, A.; Lagarón, J.M. Combining polyhydroxyalkanoates with nanokeratin to develop novel biopackaging structures. J. Appl. Polym. Sci. 2015, 133, 42695. Available online: https://onlinelibrary.wiley.com/doi/full/10.1002/app.42695 (accessed on 9 October 2022).
  73. Ali, F.B.; Kang, D.J.; Kim, M.P.; Cho, C.-H.; Kim, B.J. Synthesis of biodegradable and flexible, polylactic acid based, thermoplastic polyurethane with high gas barrier properties. Polym. Int. 2014, 63, 1620–1626. Available online: https://onlinelibrary.wiley.com/doi/full/10.1002/pi.4662 (accessed on 9 October 2022).
  74. Vostrejs, P.; Adamcová, D.; Vaverková, M.D.; Enev, V.; Kalina, M.; Machovsky, M.; Šourková, M.; Marova, I.; Kovalcik, A. Active biodegradable packaging films modified with grape seeds lignin. RSC Adv. 2020, 10, 29202–29213. Available online: https://pubmed.ncbi.nlm.nih.gov/35521111/ (accessed on 24 June 2022).
  75. Xavier, J.R.; Babusha, S.T.; George, J.; Ramana, K.V. Material Properties and Antimicrobial Activity of Polyhydroxybutyrate (PHB) Films Incorporated with Vanillin. Appl. Biochem. Biotechnol. 2015, 176, 1498–1510. Available online: https://link.springer.com/article/10.1007/s12010-015-1660-9 (accessed on 9 October 2022).
  76. Garrido-Miranda, K.A.; Rivas, B.L.; Pérez-Rivera, M.A.; Sanfuentes, E.A.; Peña-Farfal, C. Antioxidant and antifungal effects of eugenol incorporated in bionanocomposites of poly(3-hydroxybutyrate)-thermoplastic starch. LWT 2018, 98, 260–267.
  77. Liu, Y.; Low, Z.J.; Ma, X.; Liang, H.; Sinskey, A.J.; Stephanopoulos, G.; Zhou, K. Using biopolymer bodies for encapsulation of hydrophobic products in bacterium. Metab. Eng. 2020, 61, 206–214. Available online: https://pubmed.ncbi.nlm.nih.gov/32339760/ (accessed on 24 June 2022).
  78. Du, J.; Rehm, B.H.A. Purification of therapeutic proteins mediated by in vivo polyester immobilized sortase. Biotechnol. Lett. 2017, 40, 369–373. Available online: https://link.springer.com/article/10.1007/s10529-017-2473-4 (accessed on 9 October 2022).
  79. Min, K.; Park, K.; Park, D.-H.; Yoo, Y.J. Overview on the biotechnological production of l-DOPA. Appl. Microbiol. Biotechnol. 2014, 99, 575–584. Available online: https://link.springer.com/article/10.1007/s00253-014-6215-4 (accessed on 9 October 2022).
  80. Tan, D.; Zhao, J.-P.; Ran, G.-Q.; Zhu, X.-L.; Ding, Y.; Lu, X.-Y. Highly efficient biocatalytic synthesis of l-DOPA using in situ immobilized Verrucomicrobium spinosum tyrosinase on polyhydroxyalkanoate nano-granules. Appl. Microbiol. Biotechnol. 2019, 103, 5663–5678. Available online: https://pubmed.ncbi.nlm.nih.gov/31127354/ (accessed on 23 June 2022).
  81. Raberg, M.; Volodina, E.; Lin, K.; Steinbüchel, A. Ralstonia eutropha H16 in progress: Applications beside PHAs and establishment as production platform by advanced genetic tools. Crit. Rev. Biotechnol. 2017, 38, 494–510. Available online: https://www.tandfonline.com/doi/abs/10.1080/07388551.2017.1369933 (accessed on 9 October 2022).
  82. Ran, G.; Tan, D.; Dai, W.; Zhu, X.; Zhao, J.; Ma, Q.; Lu, X. Immobilization of alkaline polygalacturonate lyase from Bacillus subtilis on the surface of bacterial polyhydroxyalkanoate nano-granules. Appl. Microbiol. Biotechnol. 2017, 101, 3247–3258. Available online: https://link.springer.com/article/10.1007/s00253-016-8085-4 (accessed on 9 October 2022).
  83. Hooks, D.O.; Blatchford, P.A.; Rehm, B.H.A. Bioengineering of Bacterial Polymer Inclusions Catalyzing the Synthesis of N -Acetylneuraminic Acid. Appl. Environ. Microbiol. 2013, 79, 3116–3121. Available online: https://journals.asm.org/doi/10.1128/AEM.03947-12 (accessed on 9 October 2022).
  84. Lee, J.W.; Parlane, N.A.; Rehm, B.H.A.; Buddle, B.M.; Heiser, A. Engineering Mycobacteria for the Production of Self-Assembling Biopolyesters Displaying Mycobacterial Antigens for Use as a Tuberculosis Vaccine. Appl. Environ. Microbiol. 2017, 83, e02289-16. Available online: https://journals.asm.org/doi/10.1128/AEM.02289-16 (accessed on 9 October 2022).
  85. Wong, J.X.; Rehm, B.H.A. Design of Modular Polyhydroxyalkanoate Scaffolds for Protein Immobilization by Directed Ligation. Biomacromolecules 2018, 19, 4098–4112. Available online: https://pubs.acs.org/doi/abs/10.1021/acs.biomac.8b01093 (accessed on 10 October 2022).
  86. Wong, J.X.; Gonzalez-Miro, M.; Sutherland-Smith, A.J.; Rehm, B.H.A. Covalent Functionalization of Bioengineered Polyhydroxyalkanoate Spheres Directed by Specific Protein-Protein Interactions. Front. Bioeng. Biotechnol. 2020, 8, 44. Available online: https://pubmed.ncbi.nlm.nih.gov/32117925/ (accessed on 24 June 2022).
  87. Lassaletta, L.; Billen, G.; Grizzetti, B.; Anglade, J.; Garnier, J. 50 year trends in nitrogen use efficiency of world cropping systems: The relationship between yield and nitrogen input to cropland. Environ. Res. Lett. 2014, 9, 105011. Available online: https://iopscience.iop.org/article/10.1088/1748-9326/9/10/105011 (accessed on 9 October 2022).
  88. Luo, S.; Netravali, A. A study of physical and mechanical properties of poly(hydroxybutyrate-co-hydroxyvalerate) during composting. Polym. Degrad. Stab. 2003, 80, 59–66.
  89. Ishak, K.A.; Annuar, M.S.M.; Ahmad, N. Optimization of Water/Oil/Surfactant System for Preparation of Medium-Chain-Length Poly-3-Hydroxyalkanoates (mcl-PHA)-Incorporated Nanoparticles via Nanoemulsion Templating Technique. Appl. Biochem. Biotechnol. 2017, 16, 1191–1208. Available online: https://link.springer.com/article/10.1007/s12010-017-2492-6 (accessed on 20 June 2022).
  90. Latos-Brozio, M.; Masek, A. The Effect of Natural Additives on the Composting Properties of Aliphatic Polyesters. Polymers 2020, 12, 1856. Available online: https://pubmed.ncbi.nlm.nih.gov/32824947/ (accessed on 24 June 2022).
  91. Huerta-Angeles, G.; Brandejsová, M.; Nigmatullin, R.; Kopecká, K.; Vágnerová, H.; Šmejkalová, D.; Roy, I.; Velebný, V. Synthesis of graft copolymers based on hyaluronan and poly(3-hydroxyalkanoates). Carbohydr. Polym. 2017, 171, 220–228.
  92. Modjinou, T.; Versace, D.L.; Andaloussi, S.A.; Langlois, V.; Renard, E. Co-Networks Poly(hydroxyalkanoates)-Terpenes to Enhance Antibacterial Properties. Bioengineering 2020, 7, 13. Available online: https://pubmed.ncbi.nlm.nih.gov/31972967/ (accessed on 24 June 2022).
  93. Wang, H.L.; Gao, J.P.; Han, Y.L.; Xu, X.; Wu, R.; Gao, Y.; Cui, X.H. Comparative studies of polydatin and resveratrol on mutual transformation and antioxidative effect in vivo. Phytomedicine 2015, 22, 553–559. Available online: https://pubmed.ncbi.nlm.nih.gov/25981921/ (accessed on 9 October 2022).
  94. Latos-Brozio, M.; Masek, A. The Application of (+)-Catechin and Polydatin as Functional Additives for Biodegradable Polyesters. Int. J. Mol. Sci. 2020, 21, 414. Available online: https://pubmed.ncbi.nlm.nih.gov/31936484/ (accessed on 24 June 2022).
  95. Bhatia, S.K.; Wadhwa, P.; Hong, J.W.; Hong, Y.G.; Jeon, J.-M.; Lee, E.S.; Yang, Y.-H. Lipase mediated functionalization of poly(3-hydroxybutyrate-co-3-hydroxyvalerate) with ascorbic acid into an antioxidant active biomaterial. Int. J. Biol. Macromol. 2018, 123, 117–123. Available online: https://pubmed.ncbi.nlm.nih.gov/30428310/ (accessed on 21 June 2022).
  96. Bello-Gil, D.; Roig-Molina, E.; Fonseca, J.; Sarmiento-Ferrández, M.D.; Ferrandiz, M.; Franco, E.; Mira, E.; Maestro, B.; Sanz, J.M. An enzymatic system for decolorization of wastewater dyes using immobilized CueO laccase-like multicopper oxidase on poly-3-hydroxybutyrate. Microb. Biotechnol. 2018, 11, 881–892. Available online: https://pubmed.ncbi.nlm.nih.gov/29896867/ (accessed on 21 June 2022).
  97. Ran, G.; Tan, D.; Zhao, J.; Fan, F.; Zhang, Q.; Wu, X.; Fan, P.; Fang, X.; Lu, X. Functionalized polyhydroxyalkanoate nano-beads as a stable biocatalyst for cost-effective production of the rare sugar d-allulose. Bioresour. Technol. 2019, 289, 121673. Available online: https://pubmed.ncbi.nlm.nih.gov/31260936/ (accessed on 23 June 2022).
  98. Wang, C.; Sauvageau, D.; Elias, A. Immobilization of Active Bacteriophages on Polyhydroxyalkanoate Surfaces. ACS Appl. Mater. Interfaces 2016, 8, 1128–1138. Available online: https://pubs.acs.org/doi/abs/10.1021/acsami.5b08664 (accessed on 9 October 2022).
  99. González, E.; Herencias, C.; Prieto, M.A. A polyhydroxyalkanoate-based encapsulating strategy for ‘bioplasticizing’ microorganisms. Microb. Biotechnol. 2019, 13, 185–198. Available online: https://onlinelibrary.wiley.com/doi/full/10.1111/1751-7915.13492 (accessed on 9 October 2022).
  100. Ausejo, J.G.; Rydz, J.; Musioł, M.; Sikorska, W.; Sobota, M.; Włodarczyk, J.; Adamus, G.; Janeczek, H.; Kwiecień, I.; Hercog, A.; et al. A comparative study of three-dimensional printing directions: The degradation and toxicological profile of a PLA/PHA blend. Polym. Degrad. Stab. 2018, 152, 191–207.
  101. Pop, M.A.; Croitoru, C.; Bedo, T.; Geamăn, V.; Radomir, I.; Zaharia, S.M.; Chicoș, L.A. Influence of Internal Innovative Architecture on the Mechanical Properties of 3D Polymer Printed Parts. Polymers 2020, 12, 1129. Available online: https://pubmed.ncbi.nlm.nih.gov/32423075/ (accessed on 24 June 2022).
  102. Benson, N.U.; Bassey, D.E.; Palanisami, T. COVID pollution: Impact of COVID-19 pandemic on global plastic waste footprint. Heliyon 2021, 7, e06343. Available online: http://www.cell.com/article/S2405844021004485/fulltext (accessed on 9 October 2022).
  103. Nanda, S.; Patra, B.R.; Patel, R.; Bakos, J.; Dalai, A.K. Innovations in applications and prospects of bioplastics and biopolymers: A review. Environ. Chem. Lett. 2021, 20, 379–395. Available online: https://pubmed.ncbi.nlm.nih.gov/34867134/ (accessed on 24 June 2022).
  104. Zgodavová, K.; Lengyelová, K.; Bober, P.; Eguren, J.A.; Moreno, A. 3D Printing Optimization for Environmental Sustainability: Experimenting with Materials of Protective Face Shield Frames. Materials 2021, 14, 6595. Available online: https://pubmed.ncbi.nlm.nih.gov/34772117/ (accessed on 24 June 2022).
  105. Seggiani, M.; Cinelli, P.; Mallegni, N.; Balestri, E.; Puccini, M.; Vitolo, S.; Lardicci, C.; Lazzeri, A. materials New Bio-Composites Based on Polyhydroxyalkanoates and Posidonia oceanica Fibres for Applications in a Marine Environment. Materials 2017, 10, 326.
  106. García-Quiles, L.; Cuello, Á.F.; Castell, P. Sustainable Materials with Enhanced Mechanical Properties Based on Industrial Polyhydroxyalkanoates Reinforced with Organomodified Sepiolite and Montmorillonite. Polymers 2019, 11, 696. Available online: https://pubmed.ncbi.nlm.nih.gov/30995817/ (accessed on 23 June 2022).
  107. Yu, L.-P.; Zhang, X.; Wei, D.-X.; Wu, Q.; Jiang, X.-R.; Chen, G.-Q. Highly Efficient Fluorescent Material Based on Rare-Earth-Modified Polyhydroxyalkanoates. Biomacromolecules 2019, 20, 3233–3241. Available online: https://pubmed.ncbi.nlm.nih.gov/30624051/ (accessed on 23 June 2022).
  108. Resch-Genger, U.; Grabolle, M.; Cavaliere-Jaricot, S.; Nitschke, R.; Nann, T. Quantum dots versus organic dyes as fluorescent labels. Nat. Methods 2008, 5, 763–775. Available online: https://www.nature.com/articles/nmeth.1248 (accessed on 9 October 2022).
  109. Liu, C.; Hou, Y.; Gao, M. Are rare-earth nanoparticles suitable for in vivo applications? Adv. Mater. 2014, 26, 6922–6932. Available online: https://pubmed.ncbi.nlm.nih.gov/24616057/ (accessed on 9 October 2022).
  110. Chen, G.-Q.; Jiang, X.-R. Next generation industrial biotechnology based on extremophilic bacteria. Curr. Opin. Biotechnol. 2018, 50, 94–100.
  111. Kageyama, Y.; Tomita, H.; Isono, T.; Satoh, T.; Matsumoto, K. Artificial polyhydroxyalkanoate poly elastomer-like material. Sci. Rep. 2021, 11, 22446. Available online: https://pubmed.ncbi.nlm.nih.gov/34789822/ (accessed on 24 June 2022).
  112. Matsumoto, K.; Shiba, T.; Hiraide, Y.; Taguchi, S. Incorporation of Glycolate Units Promotes Hydrolytic Degradation in Flexible Poly(glycolate-co-3-hydroxybutyrate) Synthesized by Engineered Escherichia coli. ACS Biomater. Sci. Eng. 2016, 3, 3058–3063. Available online: https://pubs.acs.org/doi/abs/10.1021/acsbiomaterials.6b00194 (accessed on 9 October 2022).
  113. Acevedo, F.; Villegas, P.; Urtuvia, V.; Hermosilla, J.; Navia, R.; Seeger, M. Bacterial polyhydroxybutyrate for electrospun fiber production. Int. J. Biol. Macromol. 2018, 106, 692–697.
  114. Cherpinski, A.; Torres-Giner, S.; Cabedo, L.; Lagaron, J.M. Post-processing optimization of electrospun submicron poly(3-hydroxybutyrate) fibers to obtain continuous films of interest in food packaging applications. Food Addit. Contam. Part A 2017, 34, 1817–1830. Available online: https://www.tandfonline.com/doi/abs/10.1080/19440049.2017.1355115 (accessed on 20 June 2022).
  115. Cherpinski, A.; Gozutok, M.; Sasmazel, H.T.; Torres-Giner, S.; Lagaron, J.M. Electrospun Oxygen Scavenging Films of Poly(3-hydroxybutyrate) Containing Palladium Nanoparticles for Active Packaging Applications. Nanomaterials 2018, 8, 469. Available online: https://pubmed.ncbi.nlm.nih.gov/29954085/ (accessed on 21 June 2022).
  116. Mukheem, A.; Muthoosamy, K.; Manickam, S.; Sudesh, K.; Shahabuddin, S.; Saidur, R.; Akbar, N.; Sridewi, N. Fabrication and Characterization of an Electrospun PHA/Graphene Silver Nanocomposite Scaffold for Antibacterial Applications. Materials 2018, 11, 1673. Available online: https://pubmed.ncbi.nlm.nih.gov/30201852/ (accessed on 21 June 2022).
  117. Rabbani, S.; Jafari, R.; Momen, G. Superhydrophobic micro-nanofibers from PHBV-SiO2 biopolymer composites produced by electrospinning. Funct. Compos. Mater. 2022, 3, 1. Available online: https://functionalcompositematerials.springeropen.com/articles/10.1186/s42252-022-00029-5 (accessed on 15 October 2022).
  118. Kim, Y.; Kim, D.H. Pretreatment of low-grade poly(ethylene terephthalate) waste for effective depolymerization to monomers. Korean J. Chem. Eng. 2018, 35, 2303–2312. Available online: https://link.springer.com/article/10.1007/s11814-018-0130-9 (accessed on 23 November 2022).
  119. Choi, S.Y.; Na Rhie, M.; Kim, H.T.; Joo, J.C.; Cho, I.J.; Son, J.; Jo, S.Y.; Sohn, Y.J.; Baritugo, K.-A.; Pyo, J.; et al. Metabolic engineering for the synthesis of polyesters: A 100-year journey from polyhydroxyalkanoates to non-natural microbial polyesters. Metab. Eng. 2019, 58, 47–81. Available online: https://pubmed.ncbi.nlm.nih.gov/31145993/ (accessed on 23 November 2022).
  120. Rydz, J.; Sikorska, W.; Musioł, M.; Janeczek, H.; Włodarczyk, J.; Misiurska-Marczak, M.; Łęczycka, J.; Kowalczuk, M. 3D-Printed Polyester-Based Prototypes for Cosmetic Applications—Future Directions at the Forensic Engineering of Advanced Polymeric Materials. Materials 2019, 12, 994. Available online: https://pubmed.ncbi.nlm.nih.gov/30917574/ (accessed on 23 June 2022).
  121. Dorweiler, K.J.; Gurav, J.N.; Walbridge, J.S.; Ghatge, V.S.; Savant, R.H. Determination of Stability from Multicomponent Pesticide Mixes. J. Agric. Food Chem. 2016, 64, 6108–6124. Available online: https://pubmed.ncbi.nlm.nih.gov/26937779/ (accessed on 9 October 2022).
  122. Zhang, G.; Xie, W.; Wu, D. Selective localization of starch nanocrystals in the biodegradable nanocomposites probed by crystallization temperatures. Carbohydr. Polym. 2020, 227, 115341.
  123. Coltelli, M.-B.; Panariello, L.; Morganti, P.; Danti, S.; Baroni, A.; Lazzeri, A.; Fusco, A.; Donnarumma, G. Skin-Compatible Biobased Beauty Masks Prepared by Extrusion. J. Funct. Biomater. 2020, 11, 23. Available online: https://pubmed.ncbi.nlm.nih.gov/32268483/ (accessed on 24 June 2022).
  124. Rembiesa, J.; Ruzgas, T.; Engblom, J.; Holefors, A. The Impact of Pollution on Skin and Proper Efficacy Testing for Anti-Pollution Claims. Cosmetics 2018, 5, 4. Available online: https://www.mdpi.com/2079-9284/5/1/4/htm (accessed on 9 October 2022).
  125. Pacheco, G.; De Mello, C.V.; Chiari-Andréo, B.G.; Isaac, V.L.B.; Ribeiro, S.J.L.; Pecoraro, É.; Trovatti, E. Bacterial cellulose skin masks-Properties and sensory tests. J. Cosmet. Dermatol. 2017, 17, 840–847. Available online: https://pubmed.ncbi.nlm.nih.gov/28963772/ (accessed on 9 October 2022).
  126. Wu, C.S.; Liao, H.T. Interface design and reinforced features of arrowroot (Maranta arundinacea) starch/polyester-based membranes: Preparation, antioxidant activity, and cytocompatibility. Mater. Sci. Eng. C 2017, 70, 54–61.
  127. Stojanović, G.M.; Nikodinović-Runić, J.; Švenderman, S.; Kojić, T.; Radovanović, M.; Mikov, M.; Randjelović, D. Comprehensive characterization of elastomeric polyhydroxyalkanoate and its sensor applications. Mater. Sci. Eng. C Mater. Biol. Appl. 2020, 115, 111091. Available online: https://pubmed.ncbi.nlm.nih.gov/32600695/ (accessed on 24 June 2022).
  128. Benken, A.; Gianchandani, Y. Passive Wireless Pressure Sensing for Gastric Manometry. Micromachines 2019, 10, 868.
  129. Phukon, P.; Radhapyari, K.; Konwar, B.K.; Khan, R. Natural polyhydroxyalkanoate-gold nanocomposite based biosensor for detection of antimalarial drug artemisinin. Mater. Sci. Eng. C Mater. Biol. Appl. 2014, 37, 314–320. Available online: https://pubmed.ncbi.nlm.nih.gov/24582254/ (accessed on 10 October 2022).
  130. Zhang, X.; Li, Z.; Che, X.; Yu, L.; Jia, W.; Shen, R.; Chen, J.; Ma, Y.; Chen, G.Q. Synthesis and Characterization of Polyhydroxyalkanoate Organo/Hydrogels. Biomacromolecules 2019, 20, 3303–3312. Available online: https://pubmed.ncbi.nlm.nih.gov/31094501/ (accessed on 23 June 2022).
  131. Okesola, B.O.; Smith, D.K. Applying low-molecular weight supramolecular gelators in an environmental setting—Self-assembled gels as smart materials for pollutant removal. Chem. Soc. Rev. 2016, 45, 4226–4251. Available online: https://pubs.rsc.org/en/content/articlehtml/2016/cs/c6cs00124f (accessed on 9 October 2022).
  132. Babu, S.S.; Praveen, V.K.; Ajayaghosh, A. Functional π-Gelators and Their Applications. Chem. Rev. 2014, 114, 1973–2129. Available online: https://pubs.acs.org/doi/abs/10.1021/cr400195e (accessed on 9 October 2022).
  133. Zhang, K.; Liu, M.; Si, M.; Wang, Z.; Zhuo, S.; Chai, L.; Shi, Y. Polyhydroxyalkanoate-Modified Bacterium Regulates Biomass Structure and Promotes Synthesis of Carbon Materials for High-Performance Supercapacitors. ChemSusChem 2019, 12, 1732–1742. Available online: https://pubmed.ncbi.nlm.nih.gov/30793532/ (accessed on 23 June 2022).
  134. Tan, Y.; Xu, C.; Chen, G.; Liu, Z.; Ma, M.; Xie, Q.; Zheng, N.; Yao, S. Synthesis of ultrathin nitrogen-doped graphitic carbon nanocages as advanced electrode materials for supercapacitor. ACS Appl. Mater. Interfaces 2013, 5, 2241–2248. Available online: https://pubs.acs.org/doi/abs/10.1021/am400001g (accessed on 10 October 2022).
  135. Chapter 2. Wood Carbonisation and the Products it Yields. Available online: https://www.fao.org/3/x5555e/x5555e03.htm (accessed on 10 October 2022).
  136. Hindatu, Y.; Annuar, M.S.M.; Subramaniam, R.; Gumel, A.M. Medium-chain-length poly-3-hydroxyalkanoates-carbon nanotubes composite anode enhances the performance of microbial fuel cell. Bioprocess Biosyst. Eng. 2017, 40, 919–928. Available online: https://link.springer.com/article/10.1007/s00449-017-1756-4 (accessed on 20 June 2022).
  137. Szcześ, A.; Hołysz, L.; Chibowski, E. Synthesis of hydroxyapatite for biomedical applications. Adv. Colloid Interface Sci. 2017, 249, 321–330.
  138. Khasanah Reddy, K.R.; Sato, H.; Takahashi, I.; Ozaki, Y. Intermolecular hydrogen bondings in the poly(3-hydroxybutyrate) and chitin blends: Their effects on the crystallization behavior and crystal structure of poly(3-hydroxybutyrate). Polymer 2015, 75, 141–150.
  139. Faruk, O.; Bledzki, A.K.; Fink, H.-P.; Sain, M. Biocomposites reinforced with natural fibers: 2000–2010. Prog. Polym. Sci. 2012, 37, 1552–1596.
  140. Kuciel, S.; Liber-Knec, A. Biocomposites based on PHB filled with wood or kenaf fibers. Polimery 2011, 56, 218–223.
  141. Fernandes, E.G.; Pietrini, M.; Chiellini, E. Bio-Based Polymeric Composites Comprising Wood Flour as Filler. Biomacromolecules 2004, 5, 1200–1205. Available online: https://pubs.acs.org/doi/abs/10.1021/bm034507o (accessed on 10 October 2022).
  142. Arrieta, M.P.; López, J.; Hernández, A.; Rayón, E. Ternary PLA–PHB–Limonene blends intended for biodegradable food packaging applications. Eur. Polym. J. 2014, 50, 255–270.
  143. Sienkiewicz, A.; Czub, P. Flame Retardancy of Biobased Composites—Research Development. Materials 2020, 13, 5253. Available online: https://pubmed.ncbi.nlm.nih.gov/33233820/ (accessed on 24 June 2022).
  144. Gallo, E.; Schartel, B.; Acierno, D.; Russo, P. Flame retardant biocomposites: Synergism between phosphinate and nanometric metal oxides. Eur. Polym. J. 2011, 47, 1390–1401.
  145. Jiang, L.; Wolcott, M.P.; Zhang, J. Study of Biodegradable Polylactide/Poly(butylene adipate-co-terephthalate) Blends. Biomacromolecules 2005, 7, 199–207. Available online: https://pubs.acs.org/doi/abs/10.1021/bm050581q (accessed on 10 October 2022).
  146. Gallo, E.; Schartel, B.; Acierno, D.; Cimino, F.; Russo, P. Tailoring the flame retardant and mechanical performances of natural fiber-reinforced biopolymer by multi-component laminate. Compos. Part B Eng. 2013, 44, 112–119.
  147. Lapomarda, A.; Degli Esposti, M.; Micalizzi, S.; Fabbri, P.; Galletti, A.M.R.; Morselli, D.; De Maria, C. Valorization of a Levulinic Acid Platform through Electrospinning of Polyhydroxyalkanoate-Based Fibrous Membranes for In Vitro Modeling of Biological Barriers. ACS Appl. Polym. Mater. 2022, 4, 5872–5881. Available online: https://pubs.acs.org/doi/full/10.1021/acsapm.2c00721 (accessed on 15 October 2022).
  148. Wróbel-Kwiatkowska, M.; Kropiwnicki, M.; Żebrowski, J.; Beopoulos, A.; Dymińska, L.; Hanuza, J.; Rymowicz, W. Effect of mcl-PHA synthesis in flax on plant mechanical properties and cell wall composition. Transgenic Res. 2019, 28, 77–90. Available online: https://pubmed.ncbi.nlm.nih.gov/30484148/ (accessed on 21 June 2022).
  149. Sun, X.; Cheng, C.; Zhang, J.; Jin, X.; Sun, S.; Mei, L.; Huang, L. Intracellular Trafficking Network and Autophagy of PHBHHx Nanoparticles and their Implications for Drug Delivery. Sci Rep 2019, 9, 9585. Available online: https://pubmed.ncbi.nlm.nih.gov/31270337/ (accessed on 23 June 2022).
  150. Sanhueza, C.; Acevedo, F.; Rocha, S.; Villegas, P.; Seeger, M.; Navia, R. Polyhydroxyalkanoates as biomaterial for electrospun scaffolds. Int. J. Biol. Macromol. 2019, 124, 102–110. Available online: https://pubmed.ncbi.nlm.nih.gov/30445089/ (accessed on 21 June 2022).
  151. Narancic, T.; O’Connor, K.E. Plastic waste as a global challenge: Are biodegradable plastics the answer to the plastic waste problem? Microbiology 2019, 165, 129–137. Available online: https://www.microbiologyresearch.org/content/journal/micro/10.1099/mic.0.000749 (accessed on 23 November 2022).
  152. Narancic, T.; Verstichel, S.; Chaganti, S.R.; Morales-Gamez, L.; Kenny, S.T.; De Wilde, B.; Padamati, R.B.; O’Connor, K.E. Biodegradable Plastic Blends Create New Possibilities for End-of-Life Management of Plastics but They Are Not a Panacea for Plastic Pollution. Environ. Sci. Technol. 2018, 52, 10441–10452. Available online: https://pubs.acs.org/doi/abs/10.1021/acs.est.8b02963 (accessed on 23 November 2022).
  153. Qu, X.-H.; Wu, Q.; Zhang, K.-Y.; Chen, G. In vivo studies of poly(3-hydroxybutyrate-co-3-hydroxyhexanoate) based polymers: Biodegradation and tissue reactions. Biomaterials 2006, 27, 3540–3548. Available online: https://pubmed.ncbi.nlm.nih.gov/16542719/ (accessed on 23 November 2022).
  154. Samorì, C.; Galletti, P.; Giorgini, L.; Mazzeo, R.; Mazzocchetti, L.; Prati, S.; Sciutto, G.; Volpi, F.; Tagliavini, E. The Green Attitude in Art Conservation: Polyhydroxybutyrate-based Gels for the Cleaning of Oil Paintings. ChemistrySelect 2016, 1, 4502–4508. Available online: https://onlinelibrary.wiley.com/doi/full/10.1002/slct.201601180 (accessed on 9 October 2022).
  155. Jia, Y.; Sciutto, G.; Mazzeo, R.; Samorì, C.; Focarete, M.L.; Prati, S.; Gualandi, C. Organogel Coupled with Microstructured Electrospun Polymeric Nonwovens for the Effective Cleaning of Sensitive Surfaces. ACS Appl. Mater. Interfaces 2020, 12, 39620–39629. Available online: https://pubmed.ncbi.nlm.nih.gov/32820898/ (accessed on 24 June 2022).
  156. Altermann, E.; Schofield, L.R.; Ronimus, R.S.; Beattie, A.K.; Reilly, K. Inhibition of Rumen Methanogens by a Novel Archaeal Lytic Enzyme Displayed on Tailored Bionanoparticles. Front. Microbiol. 2018, 9, 2378. Available online: https://pubmed.ncbi.nlm.nih.gov/30356700/ (accessed on 21 June 2022).
More
Information
Contributors MDPI registered users' name will be linked to their SciProfiles pages. To register with us, please refer to https://encyclopedia.pub/register : ,
View Times: 1.1K
Revisions: 2 times (View History)
Update Date: 13 Dec 2022
1000/1000
Video Production Service