Thermal depolymerization: Difference between revisions
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'''Thermal depolymerization''' ('''TDP''') is the process of converting a [[polymer]] into a [[monomer]] or a mixture of monomers,<ref>{{GoldBookRef|title=Depolymerization|file = D01600}}</ref> by predominantly thermal means. It may be [[Catalysis|catalyzed]] or un-catalyzed and is distinct from other forms of [[depolymerisation|depolymerization]] which may rely on the use of chemicals or biological action. This process is associated with an increase in [[entropy]]. | '''Thermal depolymerization''' ('''TDP''') is the process of converting a [[polymer]] into a [[monomer]] or a mixture of monomers,<ref>{{GoldBookRef|title=Depolymerization|file = D01600}}</ref> by predominantly thermal means. It may be [[Catalysis|catalyzed]] or un-catalyzed and is distinct from other forms of [[depolymerisation|depolymerization]] which may rely on the use of chemicals or biological action. This process is associated with an increase in [[entropy]]. | ||
For most polymers, thermal depolymerization is chaotic process, giving a mixture of [[Volatility (chemistry)|volatile]] compounds. Materials may be depolymerized in this way during [[waste management]], with the volatile components produced being burnt as a form of [[synthetic fuel]] in a [[waste-to-energy]] process. For other polymers, thermal depolymerization is an ordered process giving a single product, or limited range of products; these transformations are usually more valuable and form the basis of some [[plastic recycling]] technologies.<ref name="Thiounn2020">{{cite journal |last1=Thiounn |first1=Timmy |last2=Smith |first2=Rhett C. |title=Advances and approaches for chemical recycling of plastic waste |journal=Journal of Polymer Science |date=15 May 2020 |volume=58 |issue=10 |pages=1347–1364 |doi=10.1002/pol.20190261|doi-access=free}}</ref> | For most polymers, thermal depolymerization is a chaotic process, giving a mixture of [[Volatility (chemistry)|volatile]] compounds. Materials may be depolymerized in this way during [[waste management]], with the volatile components produced being burnt as a form of [[synthetic fuel]] in a [[waste-to-energy]] process. For other polymers, thermal depolymerization is an ordered process giving a single product, or limited range of products; these transformations are usually more valuable and form the basis of some [[plastic recycling]] technologies.<ref name="Thiounn2020">{{cite journal |last1=Thiounn |first1=Timmy |last2=Smith |first2=Rhett C. |title=Advances and approaches for chemical recycling of plastic waste |journal=Journal of Polymer Science |date=15 May 2020 |volume=58 |issue=10 |pages=1347–1364 |doi=10.1002/pol.20190261|doi-access=free}}</ref> | ||
==Disordered depolymerization== | ==Disordered depolymerization== | ||
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===Municipal waste=== | ===Municipal waste=== | ||
Thermal treatment of [[municipal waste]] can involve the depolymerization of a very wide range of compounds, including plastics and biomass. Technologies can include simple incineration as well as pyrolysis, [[gasification]], and [[plasma gasification]]. All of these are able to accommodate mixed and contaminated feedstocks. The main advantage is the reduction in volume of the waste, particularly in densely populated areas lacking suitable sites for new [[landfill]]s. In many countries, incineration with energy recovery remains the most common method, with more advanced technologies being hindered by technical and cost hurdles.<ref>{{cite journal |title=A review on municipal solid waste-to-energy trends in the USA |journal=Renewable and Sustainable Energy Reviews |date=1 March 2020 |volume=119 | | Thermal treatment of [[municipal waste]] can involve the depolymerization of a very wide range of compounds, including plastics and biomass. Technologies can include simple incineration as well as pyrolysis, [[gasification]], and [[plasma gasification]]. All of these are able to accommodate mixed and contaminated feedstocks. The main advantage is the reduction in volume of the waste, particularly in densely populated areas lacking suitable sites for new [[landfill]]s. In many countries, incineration with energy recovery remains the most common method, with more advanced technologies being hindered by technical and cost hurdles.<ref>{{cite journal |title=A review on municipal solid waste-to-energy trends in the USA |journal=Renewable and Sustainable Energy Reviews |date=1 March 2020 |volume=119 |article-number=109512 |doi=10.1016/j.rser.2019.109512|last1=Mukherjee |first1=C. |last2=Denney |first2=J. |last3=Mbonimpa |first3=E.G. |last4=Slagley |first4=J. |last5=Bhowmik |first5=R. |s2cid=209798113 |doi-access=free |bibcode=2020RSERv.11909512M }}</ref><ref>{{cite journal |last1=Fernández-González |first1=J.M. |last2=Grindlay |first2=A.L. |last3=Serrano-Bernardo |first3=F. |last4=Rodríguez-Rojas |first4=M.I. |last5=Zamorano |first5=M. |title=Economic and environmental review of Waste-to-Energy systems for municipal solid waste management in medium and small municipalities |journal=Waste Management |date=September 2017 |volume=67 |pages=360–374 |doi=10.1016/j.wasman.2017.05.003|pmid=28501263 |bibcode=2017WaMan..67..360F }}</ref> | ||
==Ordered depolymerization== | ==Ordered depolymerization== | ||
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===Biomass=== | ===Biomass=== | ||
[[Biorefinery|Biorefineries]] convert low-value agricultural and animal waste into useful chemicals. The industrial production of [[furfural]] by the acid-catalyzed thermal treatment of [[hemicellulose]] has been in operation for over a century. [[Lignin]] has been the subject of significant research for the potential production of [[BTX (chemistry)|BTX]] and other aromatic compounds,<ref>{{cite journal |last1=Lok |first1=C.M. |last2=Van Doorn |first2=J. |last3=Aranda Almansa |first3=G. |title=Promoted ZSM-5 catalysts for the production of bio-aromatics, a review |journal=Renewable and Sustainable Energy Reviews |date=October 2019 |volume=113 | | [[Biorefinery|Biorefineries]] convert low-value agricultural and animal waste into useful chemicals. The industrial production of [[furfural]] by the acid-catalyzed thermal treatment of [[hemicellulose]] has been in operation for over a century. [[Lignin]] has been the subject of significant research for the potential production of [[BTX (chemistry)|BTX]] and other aromatic compounds,<ref>{{cite journal |last1=Lok |first1=C.M. |last2=Van Doorn |first2=J. |last3=Aranda Almansa |first3=G. |title=Promoted ZSM-5 catalysts for the production of bio-aromatics, a review |journal=Renewable and Sustainable Energy Reviews |date=October 2019 |volume=113 |article-number=109248 |doi=10.1016/j.rser.2019.109248|bibcode=2019RSERv.11309248L |s2cid=198328225 }}</ref> although such processes have not yet been commercialized with any lasting success.<ref>{{cite journal |last1=Wong |first1=Sie Shing |last2=Shu |first2=Riyang |last3=Zhang |first3=Jiaguang |last4=Liu |first4=Haichao |last5=Yan |first5=Ning |title=Downstream processing of lignin derived feedstock into end products |journal=Chemical Society Reviews |date=2020 |volume=49 |issue=15 |pages=5510–5560 |doi=10.1039/D0CS00134A|pmid=32639496 |s2cid=220405457 |url=https://eprints.lincoln.ac.uk/id/eprint/46399/1/Lignin%20Valorisation%20Review-Chem.%20Soc.%20Rev.%20Final%20version.docx |url-access=subscription }}</ref> | ||
===Plastics=== | ===Plastics=== | ||
{{Main|Plastic recycling}} | {{Main|Plastic recycling}} | ||
Certain polymers like [[PTFE]], [[Nylon 6]], [[polystyrene]], and [[polymethylmethacrylate|PMMA]]<ref>{{cite journal |last1=Kaminsky |first1=W |last2=Predel |first2=M |last3=Sadiki |first3=A |title=Feedstock recycling of polymers by pyrolysis in a fluidised bed |journal=Polymer Degradation and Stability |date=September 2004 |volume=85 |issue=3 |pages=1045–1050 |doi=10.1016/j.polymdegradstab.2003.05.002}}</ref> undergo [[depolymerization]] to give their starting [[monomers]]. These can be converted back into new plastic, a process called chemical or feedstock recycling.<ref>{{cite journal |last1=Kumagai |first1=Shogo |last2=Yoshioka |first2=Toshiaki |title=Feedstock Recycling via Waste Plastic Pyrolysis |journal=Journal of the Japan Petroleum Institute |date=1 November 2016 |volume=59 |issue=6 |pages=243–253 |doi=10.1627/jpi.59.243 |url=https://www.jstage.jst.go.jp/article/jpi/59/6/59_243/_article/-char/en|doi-access=free }}</ref><ref>{{cite journal |last1=Rahimi |first1=AliReza |last2=García |first2=Jeannette M. |title=Chemical recycling of waste plastics for new materials production |journal=Nature Reviews Chemistry |date=June 2017 |volume=1 |issue=6 | | Certain polymers like [[PTFE]], [[Nylon 6]], [[polystyrene]], and [[polymethylmethacrylate|PMMA]]<ref>{{cite journal |last1=Kaminsky |first1=W |last2=Predel |first2=M |last3=Sadiki |first3=A |title=Feedstock recycling of polymers by pyrolysis in a fluidised bed |journal=Polymer Degradation and Stability |date=September 2004 |volume=85 |issue=3 |pages=1045–1050 |doi=10.1016/j.polymdegradstab.2003.05.002}}</ref> undergo [[depolymerization]] to give their starting [[monomers]]. These can be converted back into new plastic, a process called chemical or feedstock recycling.<ref>{{cite journal |last1=Kumagai |first1=Shogo |last2=Yoshioka |first2=Toshiaki |title=Feedstock Recycling via Waste Plastic Pyrolysis |journal=Journal of the Japan Petroleum Institute |date=1 November 2016 |volume=59 |issue=6 |pages=243–253 |doi=10.1627/jpi.59.243 |url=https://www.jstage.jst.go.jp/article/jpi/59/6/59_243/_article/-char/en|doi-access=free }}</ref><ref>{{cite journal |last1=Rahimi |first1=AliReza |last2=García |first2=Jeannette M. |title=Chemical recycling of waste plastics for new materials production |journal=Nature Reviews Chemistry |date=June 2017 |volume=1 |issue=6 |page=0046 |doi=10.1038/s41570-017-0046}}</ref><ref>{{cite journal |last1=Coates |first1=Geoffrey W. |last2=Getzler |first2=Yutan D. Y. L. |title=Chemical recycling to monomer for an ideal, circular polymer economy |journal=Nature Reviews Materials |date=July 2020 |volume=5 |issue=7 |pages=501–516 |doi=10.1038/s41578-020-0190-4|bibcode=2020NatRM...5..501C |s2cid=215760966 }}</ref> In theory, this offers infinite recyclability, but it is also more expensive and has a higher [[carbon footprint]] than other forms of plastic recycling; however, in practice, this still yields an inferior product at higher energy costs than virgin polymer production in the real world because of contamination. | ||
==Related processes== | ==Related processes== | ||
Although rarely employed presently, [[coal gasification]] has historically been performed on a large scale. Thermal depolymerization is similar to other processes which use [[superheated water]] as a major phase to produce fuels, such as direct [[hydrothermal liquefaction]].<ref>{{cite web| title =Biomass Program, direct Hydrothermal Liquefaction| publisher =US Department of Energy. Energy Efficiency and Renewable Energy| date =2005-10-13| url =http://www1.eere.energy.gov/biomass/pyrolysis.html#thermal| access-date =2008-01-12 | Although rarely employed presently, [[coal gasification]] has historically been performed on a large scale. Thermal depolymerization is similar to other processes which use [[superheated water]] as a major phase to produce fuels, such as direct [[hydrothermal liquefaction]].<ref>{{cite web| title =Biomass Program, direct Hydrothermal Liquefaction| publisher =US Department of Energy. Energy Efficiency and Renewable Energy| date =2005-10-13| url =http://www1.eere.energy.gov/biomass/pyrolysis.html#thermal| access-date =2008-01-12| archive-url =https://web.archive.org/web/20070312025649/http://www1.eere.energy.gov/biomass/pyrolysis.html#thermal| archive-date =2007-03-12}}</ref> These are distinct from processes using dry materials to depolymerize, such as [[pyrolysis]]. The term ''thermochemical conversion'' (TCC) has also been used for conversion of biomass to oils, using superheated water, although it is more usually applied to fuel production via pyrolysis.<ref>{{cite journal | ||
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|access-date = 2008-02-05 | |access-date = 2008-02-05 | ||
|archive-url = https://web.archive.org/web/20080515195211/http://www.age.uiuc.edu/bee/RESEARCH/tcc/tccpaper3.htm | |archive-url = https://web.archive.org/web/20080515195211/http://www.age.uiuc.edu/bee/RESEARCH/tcc/tccpaper3.htm | ||
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| archive-url = https://web.archive.org/web/20200616024142/https://www.nvrd.nl/cms/nonexistingpage.aspx?404%3Bhttp%3A%2F%2Fwww.nvrd.nl%3A80%2Fnvrd%2Fproceedings%2FdownloadProceedings.asp%3Ffilename=618085%20Paper.pdf&filesize=85441%2F | | archive-url = https://web.archive.org/web/20200616024142/https://www.nvrd.nl/cms/nonexistingpage.aspx?404%3Bhttp%3A%2F%2Fwww.nvrd.nl%3A80%2Fnvrd%2Fproceedings%2FdownloadProceedings.asp%3Ffilename=618085%20Paper.pdf&filesize=85441%2F | ||
}}</ref> Thermal depolymerization differs in that it contains a hydrous process followed by an anhydrous cracking / distillation process. | }}</ref> Thermal depolymerization differs in that it contains a hydrous process followed by an anhydrous cracking / distillation process. | ||
[[Condensation]] polymers bearing cleavable groups such as [[ester]]s and [[amides]] can also be completely depolymerized by [[hydrolysis]] or [[solvolysis]]; this can be a purely chemical process but may also be promoted by enzymes.<ref>{{cite journal |last1=Wei |first1=Ren |last2=Zimmermann |first2=Wolfgang |title=Microbial enzymes for the recycling of recalcitrant petroleum-based plastics: how far are we? |journal=Microbial Biotechnology |date=November 2017 |volume=10 |issue=6 |pages=1308–1322 |doi=10.1111/1751-7915.12710|pmid=28371373 |pmc=5658625 }}</ref> Such technologies are less well developed than those of thermal depolymerization but have the potential for lower energy costs. Thus far,{{As of when|date=June 2024}} [[polyethylene terephthalate]] has been the most heavily studied polymer.<ref>{{cite journal |last1=Geyer |first1=B. |last2=Lorenz |first2=G. |last3=Kandelbauer |first3=A. |title=Recycling of poly(ethylene terephthalate) – A review focusing on chemical methods |journal=Express Polymer Letters |date=2016 |volume=10 |issue=7 |pages=559–586 |doi=10.3144/expresspolymlett.2016.53|doi-access=free }}</ref> It has been suggested that waste plastic could be converted into other valuable chemicals (not necessarily monomers) by microbial action,<ref>{{cite journal |last1=Ru |first1=Jiakang |last2=Huo |first2=Yixin |last3=Yang |first3=Yu |title=Microbial Degradation and Valorization of Plastic Wastes |journal=Frontiers in Microbiology |date=21 April 2020 |volume=11 | | [[Condensation]] polymers bearing cleavable groups such as [[ester]]s and [[amides]] can also be completely depolymerized by [[hydrolysis]] or [[solvolysis]]; this can be a purely chemical process but may also be promoted by enzymes.<ref>{{cite journal |last1=Wei |first1=Ren |last2=Zimmermann |first2=Wolfgang |title=Microbial enzymes for the recycling of recalcitrant petroleum-based plastics: how far are we? |journal=Microbial Biotechnology |date=November 2017 |volume=10 |issue=6 |pages=1308–1322 |doi=10.1111/1751-7915.12710|pmid=28371373 |pmc=5658625 }}</ref> Such technologies are less well developed than those of thermal depolymerization but have the potential for lower energy costs. Thus far,{{As of when|date=June 2024}} [[polyethylene terephthalate]] has been the most heavily studied polymer.<ref>{{cite journal |last1=Geyer |first1=B. |last2=Lorenz |first2=G. |last3=Kandelbauer |first3=A. |title=Recycling of poly(ethylene terephthalate) – A review focusing on chemical methods |journal=Express Polymer Letters |date=2016 |volume=10 |issue=7 |pages=559–586 |doi=10.3144/expresspolymlett.2016.53|doi-access=free }}</ref> It has been suggested that waste plastic could be converted into other valuable chemicals (not necessarily monomers) by microbial action,<ref>{{cite journal |last1=Ru |first1=Jiakang |last2=Huo |first2=Yixin |last3=Yang |first3=Yu |title=Microbial Degradation and Valorization of Plastic Wastes |journal=Frontiers in Microbiology |date=21 April 2020 |volume=11 |page=442 |doi=10.3389/fmicb.2020.00442|pmid=32373075 |pmc=7186362 |doi-access=free }}</ref><ref>{{cite journal |last1=Wierckx |first1=Nick |last2=Prieto |first2=M. Auxiliadora |last3=Pomposiello |first3=Pablo |last4=Lorenzo |first4=Victor |last5=O'Connor |first5=Kevin |last6=Blank |first6=Lars M. |title=Plastic waste as a novel substrate for industrial biotechnology |journal=Microbial Biotechnology |date=November 2015 |volume=8 |issue=6 |pages=900–903 |doi=10.1111/1751-7915.12312|pmid=26482561 |pmc=4621443 }}</ref> but such technology is still in its infancy. | ||
==See also== | ==See also== | ||
Latest revision as of 11:28, 2 October 2025
Template:Short description Thermal depolymerization (TDP) is the process of converting a polymer into a monomer or a mixture of monomers,[1] by predominantly thermal means. It may be catalyzed or un-catalyzed and is distinct from other forms of depolymerization which may rely on the use of chemicals or biological action. This process is associated with an increase in entropy.
For most polymers, thermal depolymerization is a chaotic process, giving a mixture of volatile compounds. Materials may be depolymerized in this way during waste management, with the volatile components produced being burnt as a form of synthetic fuel in a waste-to-energy process. For other polymers, thermal depolymerization is an ordered process giving a single product, or limited range of products; these transformations are usually more valuable and form the basis of some plastic recycling technologies.[2]
Disordered depolymerization
For most polymeric materials, thermal depolymerization proceeds in a disordered manner, with random chain scission giving a mixture of volatile compounds. The result is broadly akin to pyrolysis, although at higher temperatures gasification takes place. These reactions can be seen during waste management, with the products being burnt as synthetic fuel in a waste-to-energy process. In comparison to simply incinerating the starting polymer, depolymerization gives a material with a higher heating value, which can be burnt more efficiently and may also be sold. Incineration can also produce harmful dioxins and dioxin-like compounds and requires specially designed reactors and emission control systems in order to be performed safely. As the depolymerization step requires heat, it is energy-consuming; thus, the ultimate balance of energy efficiency compared to straight incineration can be very tight and has been the subject of criticism.[3]
Biomass
Many agricultural and animal wastes can be processed, but these are often already used as fertilizer, animal feed, and, in some cases, as feedstocks for paper mills or as low-quality boiler fuel. Thermal depolymerization can convert these into more economically valuable materials. Numerous biomass to liquid technologies have been developed. In general, biochemicals contain oxygen atoms, which are retained during pyrolysis, giving liquid products rich in phenols and furans.[4] These can be viewed as partially oxidized and make for low-grade fuels. Hydrothermal liquefaction technologies dehydrate the biomass during thermal processing to produce a more energy-rich product stream.[5] Similarly, gasification produces hydrogen, a very high-energy fuel.
Plastics
Plastic waste consists mostly of commodity plastics and may be actively sorted from municipal waste. Pyrolysis of mixed plastics can give a fairly broad mix of chemical products (between about 1 and 15 carbon atoms), including gases and aromatic liquids.[6] Catalysts can give a better-defined product with a higher value.[7] Likewise, hydrocracking can be employed to give LPG products. The presence of PVC can be problematic, as its thermal depolymerization generates large amounts of HCl, which can corrode equipment and cause undesirable chlorination of the products. It must be either excluded or compensated for by installing dechlorination technologies.[8] Polyethylene and polypropylene account for just less than half of global plastic production and, being pure hydrocarbons, have a higher potential for conversion to fuel.[9] Plastic-to-fuel technologies have historically struggled to be economically viable due to the costs of collecting and sorting the plastic and the relatively low value of the fuel produced.[9] Large plants are seen as being more economical than smaller ones,[10][11] but require more investment to build.
The method can, however, result in a mild net-decrease in greenhouse gas emissions,[12] though other studies dispute this. For example, a 2020 study released by Renolds on their own Hefty EnergyBag program shows net greenhouse gas emissions. The study showed then when all cradle-to-grave energy costs are tallied, burning in a cement kiln was far superior. Cement kiln fuel scored a −61.1 kg CO2 equivalents compared to +905 kg CO2 eq. It also fared far worse in terms of landfill reduction vs. kiln fuel.[13] Other studies have confirmed that plastics pyrolysis to fuel programs are also more energy intensive.[14][15]
For tire waste management, tire pyrolysis is also an option. Oil derived from tire rubber pyrolysis contains high sulfur content, which gives it high potential as a pollutant and requires hydrodesulfurization before use.[16][17] The area faces legislative, economic, and marketing obstacles.[18] In most cases, tires are simply incinerated as tire-derived fuel.
Municipal waste
Thermal treatment of municipal waste can involve the depolymerization of a very wide range of compounds, including plastics and biomass. Technologies can include simple incineration as well as pyrolysis, gasification, and plasma gasification. All of these are able to accommodate mixed and contaminated feedstocks. The main advantage is the reduction in volume of the waste, particularly in densely populated areas lacking suitable sites for new landfills. In many countries, incineration with energy recovery remains the most common method, with more advanced technologies being hindered by technical and cost hurdles.[19][20]
Ordered depolymerization
Some materials thermally decompose in an ordered manner to give a single or limited range of products. By virtue of being pure materials, they are usually more valuable than the mixtures produced by disordered thermal depolymerization. For plastics this is usually the starting monomer, and when this is recycled back into fresh polymer, it is called feedstock recycling. In practice, not all depolymerization reactions are completely efficient, and some competitive pyrolysis is often observed.
Biomass
Biorefineries convert low-value agricultural and animal waste into useful chemicals. The industrial production of furfural by the acid-catalyzed thermal treatment of hemicellulose has been in operation for over a century. Lignin has been the subject of significant research for the potential production of BTX and other aromatic compounds,[21] although such processes have not yet been commercialized with any lasting success.[22]
Plastics
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Certain polymers like PTFE, Nylon 6, polystyrene, and PMMA[23] undergo depolymerization to give their starting monomers. These can be converted back into new plastic, a process called chemical or feedstock recycling.[24][25][26] In theory, this offers infinite recyclability, but it is also more expensive and has a higher carbon footprint than other forms of plastic recycling; however, in practice, this still yields an inferior product at higher energy costs than virgin polymer production in the real world because of contamination.
Related processes
Although rarely employed presently, coal gasification has historically been performed on a large scale. Thermal depolymerization is similar to other processes which use superheated water as a major phase to produce fuels, such as direct hydrothermal liquefaction.[27] These are distinct from processes using dry materials to depolymerize, such as pyrolysis. The term thermochemical conversion (TCC) has also been used for conversion of biomass to oils, using superheated water, although it is more usually applied to fuel production via pyrolysis.[28][29] A demonstration plant due to start up in the Netherlands is said to be capable of processing 64 tons of biomass (dry basis) per day into oil.[30] Thermal depolymerization differs in that it contains a hydrous process followed by an anhydrous cracking / distillation process.
Condensation polymers bearing cleavable groups such as esters and amides can also be completely depolymerized by hydrolysis or solvolysis; this can be a purely chemical process but may also be promoted by enzymes.[31] Such technologies are less well developed than those of thermal depolymerization but have the potential for lower energy costs. Thus far,Template:As of when polyethylene terephthalate has been the most heavily studied polymer.[32] It has been suggested that waste plastic could be converted into other valuable chemicals (not necessarily monomers) by microbial action,[33][34] but such technology is still in its infancy.
See also
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References
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- ↑ IUPAC, Compendium of Chemical Terminology, 5th ed. (the "Gold Book") (2025). Online version: (2006–) "Depolymerization". Script error: No such module "CS1 identifiers".Script error: No such module "TemplatePar".
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- ↑ Ringer, M.; Putsche, V.; Scahill, J. (2006) Large-Scale Pyrolysis Oil Production: A Technology Assessment and Economic Analysis Script error: No such module "webarchive".; NREL/TP-510-37779; National Renewable Energy Laboratory (NREL), Golden, CO.
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