Using a flame ionisation detector to measure the rate and duration of pyrolysis of a biomass particle
Single cubes and spheres of spruce wood have been heated in beds of inert sand, fluidised by nitrogen and heated electrically to 500–700 °C. The release of volatile matter from these pyrolysing particles, submerged inside a cage in the bed, was monitored by continuously sampling the off-gas from the...
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description | Single cubes and spheres of spruce wood have been heated in beds of inert sand, fluidised by nitrogen and heated electrically to 500–700 °C. The release of volatile matter from these pyrolysing particles, submerged inside a cage in the bed, was monitored by continuously sampling the off-gas from the bed into a rapid, flame ionisation detector (FID). This instrument's output was shown to be proportional to the rate at which carbonaceous volatile species were produced by a wooden particle, when thermally decomposing in the hot fluidised bed. The FID's rapid response revealed that some volatiles were released in brief, explosive bursts (lasting ~ 1 s), probably after local build-ups of pressure inside the biomass. Interestingly, the production of volatiles continued after the centre of a decomposing particle had reached the bed's temperature. Thus, the FID provided good measurements of pyrolysis times. The measurements also indicated that volatiles appeared in a fluidised bed as a cloud of bubbles rising around a decomposing particle. The bubbles pushed away the hot sand and so markedly reduced the rate of heat transfer from the bed to a particle. This had unexpected consequences. In a hot bed (700 °C), the duration of pyrolysis for a cube of spruce was proportional to the length, L, of the cube's side, for L ≤ 7 mm. This means that external heat transfer, which included radiation from the bed, then controlled the rate of thermal decomposition. In a cooler bed (500 °C), the duration of pyrolysis depended on a mix of L and L2, indicating that control was then by both internal and external heat transfer. Thus, from 500 to 700 °C bubbles of volatiles increasingly inhibited external heat transfer from the bed to a pyrolysing particle. Also, at 700 °C, the bed's radiation was largely absorbed by the products of pyrolysis inside the bubbles. After a particle's centre had reached the bed's temperature, volatiles continued to appear slowly at a rate, probably controlled by chemical kinetics. The identity of the rate-determining step is discussed for spruce particles of different sizes and beds at various temperatures. However, it is clear that the FID, with its rapid response and sensitivity, revealed new details of the pyrolysis of small particles (2 – 7 mm) of wood in a fluidised bed. For example, the thermal decomposition of spruce involves at least two separate, endothermic reactions and a final, exothermic step. |
doi_str_mv | 10.1016/j.combustflame.2021.111438 |
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The release of volatile matter from these pyrolysing particles, submerged inside a cage in the bed, was monitored by continuously sampling the off-gas from the bed into a rapid, flame ionisation detector (FID). This instrument's output was shown to be proportional to the rate at which carbonaceous volatile species were produced by a wooden particle, when thermally decomposing in the hot fluidised bed. The FID's rapid response revealed that some volatiles were released in brief, explosive bursts (lasting ~ 1 s), probably after local build-ups of pressure inside the biomass. Interestingly, the production of volatiles continued after the centre of a decomposing particle had reached the bed's temperature. Thus, the FID provided good measurements of pyrolysis times. The measurements also indicated that volatiles appeared in a fluidised bed as a cloud of bubbles rising around a decomposing particle. The bubbles pushed away the hot sand and so markedly reduced the rate of heat transfer from the bed to a particle. This had unexpected consequences. In a hot bed (700 °C), the duration of pyrolysis for a cube of spruce was proportional to the length, L, of the cube's side, for L ≤ 7 mm. This means that external heat transfer, which included radiation from the bed, then controlled the rate of thermal decomposition. In a cooler bed (500 °C), the duration of pyrolysis depended on a mix of L and L2, indicating that control was then by both internal and external heat transfer. Thus, from 500 to 700 °C bubbles of volatiles increasingly inhibited external heat transfer from the bed to a pyrolysing particle. Also, at 700 °C, the bed's radiation was largely absorbed by the products of pyrolysis inside the bubbles. After a particle's centre had reached the bed's temperature, volatiles continued to appear slowly at a rate, probably controlled by chemical kinetics. The identity of the rate-determining step is discussed for spruce particles of different sizes and beds at various temperatures. However, it is clear that the FID, with its rapid response and sensitivity, revealed new details of the pyrolysis of small particles (2 – 7 mm) of wood in a fluidised bed. For example, the thermal decomposition of spruce involves at least two separate, endothermic reactions and a final, exothermic step.</description><identifier>ISSN: 0010-2180</identifier><identifier>EISSN: 1556-2921</identifier><identifier>DOI: 10.1016/j.combustflame.2021.111438</identifier><language>eng</language><publisher>New York: Elsevier Inc</publisher><subject>Biomass ; Bubbles ; Cubes ; Decomposition reactions ; Endothermic reactions ; Exothermic reactions ; Flame ionization detectors ; Fluidized beds ; Heat transfer ; Heat transfer in fluidised beds ; Kinetics of thermal decomposition of biomass ; Measurement of pyrolysis times ; Pyrolysis ; Radiation ; Rate of pyrolysis of a wood ; Reaction kinetics ; Sand ; Thermal decomposition ; Volatile compounds ; Wood and biomass</subject><ispartof>Combustion and flame, 2021-08, Vol.230, p.111438, Article 111438</ispartof><rights>2021 The Combustion Institute</rights><rights>Copyright Elsevier BV Aug 2021</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c352t-fec91a15e4e9bcc564099eff905eee3c263831ca18de42e10428256bd513fc443</citedby><cites>FETCH-LOGICAL-c352t-fec91a15e4e9bcc564099eff905eee3c263831ca18de42e10428256bd513fc443</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/j.combustflame.2021.111438$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,777,781,3537,27905,27906,45976</link.rule.ids></links><search><creatorcontrib>Volford, Andras</creatorcontrib><creatorcontrib>Redko, Thomas</creatorcontrib><creatorcontrib>Marek, Ewa J.</creatorcontrib><creatorcontrib>Bond, Zach.W.M.</creatorcontrib><creatorcontrib>Hayhurst, Allan N.</creatorcontrib><title>Using a flame ionisation detector to measure the rate and duration of pyrolysis of a biomass particle</title><title>Combustion and flame</title><description>Single cubes and spheres of spruce wood have been heated in beds of inert sand, fluidised by nitrogen and heated electrically to 500–700 °C. The release of volatile matter from these pyrolysing particles, submerged inside a cage in the bed, was monitored by continuously sampling the off-gas from the bed into a rapid, flame ionisation detector (FID). This instrument's output was shown to be proportional to the rate at which carbonaceous volatile species were produced by a wooden particle, when thermally decomposing in the hot fluidised bed. The FID's rapid response revealed that some volatiles were released in brief, explosive bursts (lasting ~ 1 s), probably after local build-ups of pressure inside the biomass. Interestingly, the production of volatiles continued after the centre of a decomposing particle had reached the bed's temperature. Thus, the FID provided good measurements of pyrolysis times. The measurements also indicated that volatiles appeared in a fluidised bed as a cloud of bubbles rising around a decomposing particle. The bubbles pushed away the hot sand and so markedly reduced the rate of heat transfer from the bed to a particle. This had unexpected consequences. In a hot bed (700 °C), the duration of pyrolysis for a cube of spruce was proportional to the length, L, of the cube's side, for L ≤ 7 mm. This means that external heat transfer, which included radiation from the bed, then controlled the rate of thermal decomposition. In a cooler bed (500 °C), the duration of pyrolysis depended on a mix of L and L2, indicating that control was then by both internal and external heat transfer. Thus, from 500 to 700 °C bubbles of volatiles increasingly inhibited external heat transfer from the bed to a pyrolysing particle. Also, at 700 °C, the bed's radiation was largely absorbed by the products of pyrolysis inside the bubbles. After a particle's centre had reached the bed's temperature, volatiles continued to appear slowly at a rate, probably controlled by chemical kinetics. The identity of the rate-determining step is discussed for spruce particles of different sizes and beds at various temperatures. However, it is clear that the FID, with its rapid response and sensitivity, revealed new details of the pyrolysis of small particles (2 – 7 mm) of wood in a fluidised bed. For example, the thermal decomposition of spruce involves at least two separate, endothermic reactions and a final, exothermic step.</description><subject>Biomass</subject><subject>Bubbles</subject><subject>Cubes</subject><subject>Decomposition reactions</subject><subject>Endothermic reactions</subject><subject>Exothermic reactions</subject><subject>Flame ionization detectors</subject><subject>Fluidized beds</subject><subject>Heat transfer</subject><subject>Heat transfer in fluidised beds</subject><subject>Kinetics of thermal decomposition of biomass</subject><subject>Measurement of pyrolysis times</subject><subject>Pyrolysis</subject><subject>Radiation</subject><subject>Rate of pyrolysis of a wood</subject><subject>Reaction kinetics</subject><subject>Sand</subject><subject>Thermal decomposition</subject><subject>Volatile compounds</subject><subject>Wood and biomass</subject><issn>0010-2180</issn><issn>1556-2921</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2021</creationdate><recordtype>article</recordtype><recordid>eNqNkE9LxDAUxIMouK5-h6Dn1ryk6bbexP-w4MU9hzR91ZS2qUkq7Le3az149DQMzMzj_Qi5BJYCg_y6TY3rqynEptM9ppxxSAEgE8URWYGUecJLDsdkxRiwhEPBTslZCC1jbJMJsSK4C3Z4p5r-DFDrBht0nIXWGNFE52l0tEcdJo80fiD1OiLVQ03ryS9J19Bx7123DzYcjKaVdb0OgY7aR2s6PCcnje4CXvzqmuweH97unpPt69PL3e02MULymDRoStAgMcOyMkbmGStLbJqSSUQUhueiEGA0FDVmHIFlvOAyr2oJojFZJtbkatkdvfucMETVuskP80nFpYQNcFbAnLpZUsa7EDw2avS2136vgKkDVtWqv1jVAatasM7l-6WM8x9fFr0KxuJgsLZ-5qVqZ_8z8w3Rp4jA</recordid><startdate>202108</startdate><enddate>202108</enddate><creator>Volford, Andras</creator><creator>Redko, Thomas</creator><creator>Marek, Ewa J.</creator><creator>Bond, Zach.W.M.</creator><creator>Hayhurst, Allan N.</creator><general>Elsevier Inc</general><general>Elsevier BV</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7TB</scope><scope>8FD</scope><scope>FR3</scope><scope>H8D</scope><scope>L7M</scope></search><sort><creationdate>202108</creationdate><title>Using a flame ionisation detector to measure the rate and duration of pyrolysis of a biomass particle</title><author>Volford, Andras ; Redko, Thomas ; Marek, Ewa J. ; Bond, Zach.W.M. ; Hayhurst, Allan N.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c352t-fec91a15e4e9bcc564099eff905eee3c263831ca18de42e10428256bd513fc443</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2021</creationdate><topic>Biomass</topic><topic>Bubbles</topic><topic>Cubes</topic><topic>Decomposition reactions</topic><topic>Endothermic reactions</topic><topic>Exothermic reactions</topic><topic>Flame ionization detectors</topic><topic>Fluidized beds</topic><topic>Heat transfer</topic><topic>Heat transfer in fluidised beds</topic><topic>Kinetics of thermal decomposition of biomass</topic><topic>Measurement of pyrolysis times</topic><topic>Pyrolysis</topic><topic>Radiation</topic><topic>Rate of pyrolysis of a wood</topic><topic>Reaction kinetics</topic><topic>Sand</topic><topic>Thermal decomposition</topic><topic>Volatile compounds</topic><topic>Wood and biomass</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Volford, Andras</creatorcontrib><creatorcontrib>Redko, Thomas</creatorcontrib><creatorcontrib>Marek, Ewa J.</creatorcontrib><creatorcontrib>Bond, Zach.W.M.</creatorcontrib><creatorcontrib>Hayhurst, Allan N.</creatorcontrib><collection>CrossRef</collection><collection>Mechanical & Transportation Engineering Abstracts</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>Aerospace Database</collection><collection>Advanced Technologies Database with Aerospace</collection><jtitle>Combustion and flame</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Volford, Andras</au><au>Redko, Thomas</au><au>Marek, Ewa J.</au><au>Bond, Zach.W.M.</au><au>Hayhurst, Allan N.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Using a flame ionisation detector to measure the rate and duration of pyrolysis of a biomass particle</atitle><jtitle>Combustion and flame</jtitle><date>2021-08</date><risdate>2021</risdate><volume>230</volume><spage>111438</spage><pages>111438-</pages><artnum>111438</artnum><issn>0010-2180</issn><eissn>1556-2921</eissn><abstract>Single cubes and spheres of spruce wood have been heated in beds of inert sand, fluidised by nitrogen and heated electrically to 500–700 °C. The release of volatile matter from these pyrolysing particles, submerged inside a cage in the bed, was monitored by continuously sampling the off-gas from the bed into a rapid, flame ionisation detector (FID). This instrument's output was shown to be proportional to the rate at which carbonaceous volatile species were produced by a wooden particle, when thermally decomposing in the hot fluidised bed. The FID's rapid response revealed that some volatiles were released in brief, explosive bursts (lasting ~ 1 s), probably after local build-ups of pressure inside the biomass. Interestingly, the production of volatiles continued after the centre of a decomposing particle had reached the bed's temperature. Thus, the FID provided good measurements of pyrolysis times. The measurements also indicated that volatiles appeared in a fluidised bed as a cloud of bubbles rising around a decomposing particle. The bubbles pushed away the hot sand and so markedly reduced the rate of heat transfer from the bed to a particle. This had unexpected consequences. In a hot bed (700 °C), the duration of pyrolysis for a cube of spruce was proportional to the length, L, of the cube's side, for L ≤ 7 mm. This means that external heat transfer, which included radiation from the bed, then controlled the rate of thermal decomposition. In a cooler bed (500 °C), the duration of pyrolysis depended on a mix of L and L2, indicating that control was then by both internal and external heat transfer. Thus, from 500 to 700 °C bubbles of volatiles increasingly inhibited external heat transfer from the bed to a pyrolysing particle. Also, at 700 °C, the bed's radiation was largely absorbed by the products of pyrolysis inside the bubbles. After a particle's centre had reached the bed's temperature, volatiles continued to appear slowly at a rate, probably controlled by chemical kinetics. The identity of the rate-determining step is discussed for spruce particles of different sizes and beds at various temperatures. However, it is clear that the FID, with its rapid response and sensitivity, revealed new details of the pyrolysis of small particles (2 – 7 mm) of wood in a fluidised bed. For example, the thermal decomposition of spruce involves at least two separate, endothermic reactions and a final, exothermic step.</abstract><cop>New York</cop><pub>Elsevier Inc</pub><doi>10.1016/j.combustflame.2021.111438</doi></addata></record> |
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subjects | Biomass Bubbles Cubes Decomposition reactions Endothermic reactions Exothermic reactions Flame ionization detectors Fluidized beds Heat transfer Heat transfer in fluidised beds Kinetics of thermal decomposition of biomass Measurement of pyrolysis times Pyrolysis Radiation Rate of pyrolysis of a wood Reaction kinetics Sand Thermal decomposition Volatile compounds Wood and biomass |
title | Using a flame ionisation detector to measure the rate and duration of pyrolysis of a biomass particle |
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