2015
DOI: 10.1016/j.applthermaleng.2015.04.070
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New energy value chain through pyrolysis of hospital plastic waste

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Cited by 47 publications
(14 citation statements)
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References 29 publications
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“…The liquid was collected in a glass vessel (6) immersed in an ice bucket (7) while incondensable products passed into a glass collector system to ensure optimal sampling, and then discharged. The bench installation has been already successfully used by the team for thermal and catalytic cracking of biomass tar, plastic wastes, and industrial fatty residues [23][24][25].…”
Section: Bench-scale Installationmentioning
confidence: 99%
“…The liquid was collected in a glass vessel (6) immersed in an ice bucket (7) while incondensable products passed into a glass collector system to ensure optimal sampling, and then discharged. The bench installation has been already successfully used by the team for thermal and catalytic cracking of biomass tar, plastic wastes, and industrial fatty residues [23][24][25].…”
Section: Bench-scale Installationmentioning
confidence: 99%
“…A 63 similar effect was observed working at high heating rates. 64 Paraschiv et al(2015) studied the pyrolysis of five common polymers present in hospital plastic 65 waste in three different fixed bed reactor scales in order to maximize the production of the 66 condensable fraction and optimize its energetic properties. The authors began with the 67 thermogravimetric analysis (TGA) of each polymer and the data obtained in this study were 68 employed to adapt the cooler system of the laboratory reactor to achieve the complete 69 condensation of pyrolysis vapors.…”
Section: Non-viscoelastic Polyurethane Foam 56mentioning
confidence: 99%
“…The Ti values of the PP and PE coastal debris showed lower initial pyrolysis temperatures than in other studies [30][31][32][33]. The initiation of thermal decomposition for PP occurred at a lower temperature than for PE because the polymer chain of the PP coastal debris sample consists of a tertiary carbon, which corresponds to branching [13,29]. Furthermore, Tm increased from 434.98 °C to 464.98 °C for the nylon, from 474.97 °C to 499.96 °C for the PE, from 455.02 °C to 475.97 °C for the PP, and from 360.00 °C to 374.90 °C for the wood (bamboo) coastal debris sample.…”
Section: Effect Of the Heating Rate On The Pyrolysis Process Of Coastmentioning
confidence: 68%
“…Accordingly, to reduce the resistance, samples with a small particle size were selected for all the experiments. The effluences of the heating rate were a significant factor in the pyrolysis due to the variations of the heat and mass transfer inside or among the sample particles [27,29]. Table 2.…”
Section: Effect Of the Heating Rate On The Pyrolysis Process Of Coastmentioning
confidence: 99%