Morphology of Penicillium funiculosum During Biodegradation of Poly (β-hydroxybutyrate-co-β-hydroxyvalerate) [PHBV] with Poly (ε-Caprolactone) [PCL] Blends
Blends of poly (β-hydroxybutyrate-co-β-hydroxyvalerate) with poly (ε-caprolactone) were produced using melt mixing and solvent casting techniques. The biodegradation of blends was tested based in the ASTM G21-90 using Penicillium funiculosum fungal specie. The CO 2 production during biodegradation w...
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Published in: | Journal of polymers and the environment Vol. 19; no. 4; pp. 834 - 840 |
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Language: | English |
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Abstract | Blends of poly (β-hydroxybutyrate-co-β-hydroxyvalerate) with poly (ε-caprolactone) were produced using melt mixing and solvent casting techniques. The biodegradation of blends was tested based in the ASTM G21-90 using
Penicillium funiculosum
fungal specie. The CO
2
production during biodegradation was measured and fitted using the Gompertz model. Biodegradation of blends varies according to the mixing technique and the proportion of bacterial polymers in the blends. Although lag phase was larger, solvent-casted blends were easier to degrade due to their porous surface and relative lower crystallinity.
P. funiculosum
morphology during biodegradation appeared to be related to carbon availability i.e. larger and more complex conidiophores, more phialides per conidiophore and the presence of double-phialides, were found in blends with higher PHAs proportion.
P. funiculosum
morphology was independent to the blending technique used. Hence, morphology of
P. funiculosum
could be useful as a reference for carbon bioavailability of the blends. |
---|---|
AbstractList | Blends of poly ( beta -hydroxybutyrate-co- beta -hydroxyvalerate) with poly ( epsilon -caprolactone) were produced using melt mixing and solvent casting techniques. The biodegradation of blends was tested based in the ASTM G21-90 using Penicillium funiculosum fungal specie. The CO sub(2) production during biodegradation was measured and fitted using the Gompertz model. Biodegradation of blends varies according to the mixing technique and the proportion of bacterial polymers in the blends. Although lag phase was larger, solvent-casted blends were easier to degrade due to their porous surface and relative lower crystallinity. P. funiculosum morphology during biodegradation appeared to be related to carbon availability i.e. larger and more complex conidiophores, more phialides per conidiophore and the presence of double-phialides, were found in blends with higher PHAs proportion. P. funiculosum morphology was independent to the blending technique used. Hence, morphology of P. funiculosum could be useful as a reference for carbon bioavailability of the blends. Blends of poly (β-hydroxybutyrate-co-β-hydroxyvalerate) with poly (ε-caprolactone) were produced using melt mixing and solvent casting techniques. The biodegradation of blends was tested based in the ASTM G21-90 using Penicillium funiculosum fungal specie. The CO 2 production during biodegradation was measured and fitted using the Gompertz model. Biodegradation of blends varies according to the mixing technique and the proportion of bacterial polymers in the blends. Although lag phase was larger, solvent-casted blends were easier to degrade due to their porous surface and relative lower crystallinity. P. funiculosum morphology during biodegradation appeared to be related to carbon availability i.e. larger and more complex conidiophores, more phialides per conidiophore and the presence of double-phialides, were found in blends with higher PHAs proportion. P. funiculosum morphology was independent to the blending technique used. Hence, morphology of P. funiculosum could be useful as a reference for carbon bioavailability of the blends. Blends of poly (β-hydroxybutyrate-co-β-hydroxyvalerate) with poly ([straight epsilon]-caprolactone) were produced using melt mixing and solvent casting techniques. The biodegradation of blends was tested based in the ASTM G21-90 using Penicillium funiculosum fungal specie. The CO2 production during biodegradation was measured and fitted using the Gompertz model. Biodegradation of blends varies according to the mixing technique and the proportion of bacterial polymers in the blends. Although lag phase was larger, solvent-casted blends were easier to degrade due to their porous surface and relative lower crystallinity. P. funiculosum morphology during biodegradation appeared to be related to carbon availability i.e. larger and more complex conidiophores, more phialides per conidiophore and the presence of double-phialides, were found in blends with higher PHAs proportion. P. funiculosum morphology was independent to the blending technique used. Hence, morphology of P. funiculosum could be useful as a reference for carbon bioavailability of the blends.[PUBLICATION ABSTRACT] |
Author | Gracida-Rodríguez, Jorge Noel Vergara-Porras, Berenice Pérez-Guevara, Fermín |
Author_xml | – sequence: 1 givenname: Berenice surname: Vergara-Porras fullname: Vergara-Porras, Berenice organization: Biotechnology and Bioengineering Department, CINVESTAV-IPN – sequence: 2 givenname: Jorge Noel surname: Gracida-Rodríguez fullname: Gracida-Rodríguez, Jorge Noel organization: Biotechnology Department, Universidad Politécnica de Pachuca – sequence: 3 givenname: Fermín surname: Pérez-Guevara fullname: Pérez-Guevara, Fermín email: fermin@cinvestav.mx organization: Biotechnology and Bioengineering Department, CINVESTAV-IPN |
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Cites_doi | 10.1016/S0964-8305(02)00177-4 10.1128/AEM.56.6.1875-1881.1990 10.1016/j.molcatb.2010.05.004 10.1021/ma961431y 10.1517/17425240802583421 10.1002/(SICI)1097-0290(19960105)49:1<1::AID-BIT1>3.3.CO;2-1 10.1016/j.ejsobi.2008.12.002 10.1016/S0045-6535(01)00199-0 10.1016/j.biotechadv.2003.09.005 10.1016/S0079-6700(01)00050-8 10.1002/app.1995.070550212 10.1016/j.polymdegradstab.2004.09.013 10.1016/S0032-3861(99)00534-0 10.1007/s11274-005-9098-9 10.1016/j.biomaterials.2005.01.071 10.1021/ma00031a008 10.1021/es803329p 10.1016/j.polymer.2007.08.033 10.2174/138920007782109823 10.1002/pi.858 10.1016/j.tca.2005.01.060 10.1023/A:1015245710406 10.1016/S1369-5274(02)00338-7 10.1897/05-458R.1 10.1016/S0141-3910(98)00092-5 10.1016/j.polymer.2005.10.058 10.1016/S1701-2163(16)34118-4 10.1016/S0378-4371(02)01249-9 10.1007/s00253-002-1205-3 10.1016/S0079-6700(02)00149-1 |
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Snippet | Blends of poly (β-hydroxybutyrate-co-β-hydroxyvalerate) with poly (ε-caprolactone) were produced using melt mixing and solvent casting techniques. The... Blends of poly (β-hydroxybutyrate-co-β-hydroxyvalerate) with poly ([straight epsilon]-caprolactone) were produced using melt mixing and solvent casting... Blends of poly ( beta -hydroxybutyrate-co- beta -hydroxyvalerate) with poly ( epsilon -caprolactone) were produced using melt mixing and solvent casting... |
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SubjectTerms | Bacteria Bioavailability Biodegradation Blends Carbon Carbon dioxide Chemistry Chemistry and Materials Science Environmental Chemistry Environmental Engineering/Biotechnology Fungi Industrial Chemistry/Chemical Engineering Materials Science Morphology Original Paper Penicillium funiculosum Polymer blends Polymer Sciences Polymers Solvents |
Title | Morphology of Penicillium funiculosum During Biodegradation of Poly (β-hydroxybutyrate-co-β-hydroxyvalerate) [PHBV] with Poly (ε-Caprolactone) [PCL] Blends |
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