2022
DOI: 10.1016/j.jcomc.2022.100253
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Reducing the environmental impacts of plastics while increasing strength: Biochar fillers in biodegradable, recycled, and fossil-fuel derived plastics

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Cited by 19 publications
(11 citation statements)
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“…Certain biopolymers containing ester bonds in their structures, such as poly­(lactide) (PLA) or poly­(3-hydroxybutyrate) (PHB), are primarily used in various applications such as a material for food packaging, clothing, particular functional components, automotive, agricultural uses, or specific medicinal purposes with the incorporation of FDM 3D printing technology . Once these biopolymer structures reach their functional limit, often determined by their molecular weight decrease or a state of visual degradation, they cannot be effectively mechanically recycled and used for material production due to their considerably lower quality and worse properties compared to a virgin polymer manufactured for the first time. The chemical structure of PLA and P3HB can lead to a promising molecule reuse idea: the ester bonds of partially degraded and materially unusable macromolecules can undergo a transesterification reaction using alcohols such as methanol or ethanol as a nucleophile, resulting in a process called chemical recycling. This idea clarifies the possibility of taking advantage of the biopolymers’ further state of structure degradation as an opportunity to be depolymerized to monomer alkyl esters, which can serve completely new purposes compared to virgin macromolecules. These products can serve as biobased solvents, extraction systems, or dispersion continua .…”
Section: Introductionmentioning
confidence: 99%
“…Certain biopolymers containing ester bonds in their structures, such as poly­(lactide) (PLA) or poly­(3-hydroxybutyrate) (PHB), are primarily used in various applications such as a material for food packaging, clothing, particular functional components, automotive, agricultural uses, or specific medicinal purposes with the incorporation of FDM 3D printing technology . Once these biopolymer structures reach their functional limit, often determined by their molecular weight decrease or a state of visual degradation, they cannot be effectively mechanically recycled and used for material production due to their considerably lower quality and worse properties compared to a virgin polymer manufactured for the first time. The chemical structure of PLA and P3HB can lead to a promising molecule reuse idea: the ester bonds of partially degraded and materially unusable macromolecules can undergo a transesterification reaction using alcohols such as methanol or ethanol as a nucleophile, resulting in a process called chemical recycling. This idea clarifies the possibility of taking advantage of the biopolymers’ further state of structure degradation as an opportunity to be depolymerized to monomer alkyl esters, which can serve completely new purposes compared to virgin macromolecules. These products can serve as biobased solvents, extraction systems, or dispersion continua .…”
Section: Introductionmentioning
confidence: 99%
“…6 , the pure HDPE has lower peaks compared with blended biochar/HDPE composites, and this can lead to conclude that most functional groups (peaks) of the composites are developed due to the addition of the pine wood biochar. From the FTIR analysis, almost no new functional groups or change of functional groups are observed due to the hot molding process [ 56 ]. However, the FTIR analysis of the un-pyrolyzed pine wood biochar/HDPE composites showed different peaks due to the presence of volatile matter, ash and other residues that need to be removed during pyrolysis [ 57 ].…”
Section: Resultsmentioning
confidence: 99%
“…Therefore, the biodegradability of the pure CMC film and CMC film containing chitosan and cellulose derivatives was evaluated ( Figure 6 ). To enhance the biodegradability of CMC, natural plasticizers were added, including bio-based polylactic acid (PLA) as a control to compare the level of biodegradability with other known biodegradable materials [ 52 , 53 ]. After a testing period of 35 days, the accumulated CO 2 (mg) values were determined as follows: 264.92 for CMC film, 281.45 for CMC/O-CMCh film, 287.78 for CMC/HTCMCh film, 289.08 for CMC/HACC film, 290.46 for CMC/CNC, 296.12 for CMC/CNF, and 108.83 for PLA.…”
Section: Resultsmentioning
confidence: 99%