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Enabling resource circularity through thermo-catalytic and solvent-based conversion of waste plastics

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Abstract

The recent rise in plastic pollution has led to a growing environmental burden, motivating new and effective methods for circular repurposing of “end-of-use” plastics. In this review, we highlight recent advances in thermochemical and catalytic pathways toward circularity of plastics utilization; specifically, hydroconversion, solvent conversion, and catalytic conversion without solvent or gaseous reagent. We present advances in the design of supported metal catalysts (Pt, Ru, Zr) for the hydroconversion of plastics, especially polyolefins (POs) and polyesters. We deduce mechanistic insights from hydroconversion reactions toward realizing economic circularity. We also review two solvent treatments: solvolysis of condensation polymers and solvent extraction for composite polymers. Last, we discuss advances in hydrocarbon conversion, without solvent or gaseous reagent, to catalytically depolymerize POs. We highlight the challenges and envision the path forward in optimal catalyst and process design that will enable the development of chemical upcycling technologies for building a circular plastic economy.

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... While several excellent reviews have been published in recent years on depolymerization of plastics by heterogeneous catalysis, 11,12 the importance of interfacial processes for plastics degradation, recycling, and upcycling is just starting to be recognized, leading to novel insights into the kinetics and design of such reactions. Thus, we spotlight the need to better characterize and study these phenomena in this Perspective. ...
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... Solvolysis is the chemical breaking of bonds in the presence of a solvent [79], and as such is a synonym for depolymerization. The term is sometimes misused to describe solvent-based recycling [47,52,80]; at times, depolymerization processes have even been described as solvent-based [81]. ...
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Methods: Topic-focused reviews that examine the effects of ocean pollution on human health, identify gaps in knowledge, project future trends, and offer evidence-based guidance for effective intervention. Environmental Findings: Pollution of the oceans is widespread, worsening, and in most countries poorly controlled. It is a complex mixture of toxic metals, plastics, manufactured chemicals, petroleum, urban and industrial wastes, pesticides, fertilizers, pharmaceutical chemicals, agricultural runoff, and sewage. More than 80% arises from land-based sources. It reaches the oceans through rivers, runoff, atmospheric deposition and direct discharges. It is often heaviest near the coasts and most highly concentrated along the coasts of low- and middle-income countries. Plastic is a rapidly increasing and highly visible component of ocean pollution, and an estimated 10 million metric tons of plastic waste enter the seas each year. Mercury is the metal pollutant of greatest concern in the oceans; it is released from two main sources – coal combustion and small-scale gold mining. Global spread of industrialized agriculture with increasing use of chemical fertilizer leads to extension of Harmful Algal Blooms (HABs) to previously unaffected regions. Chemical pollutants are ubiquitous and contaminate seas and marine organisms from the high Arctic to the abyssal depths. Ecosystem Findings: Ocean pollution has multiple negative impacts on marine ecosystems, and these impacts are exacerbated by global climate change. Petroleum-based pollutants reduce photosynthesis in marine microorganisms that generate oxygen. Increasing absorption of carbon dioxide into the seas causes ocean acidification, which destroys coral reefs, impairs shellfish development, dissolves calcium-containing microorganisms at the base of the marine food web, and increases the toxicity of some pollutants. Plastic pollution threatens marine mammals, fish, and seabirds and accumulates in large mid-ocean gyres. It breaks down into microplastic and nanoplastic particles containing multiple manufactured chemicals that can enter the tissues of marine organisms, including species consumed by humans. Industrial releases, runoff, and sewage increase frequency and severity of HABs, bacterial pollution, and anti-microbial resistance. Pollution and sea surface warming are triggering poleward migration of dangerous pathogens such as the Vibrio species. Industrial discharges, pharmaceutical wastes, pesticides, and sewage contribute to global declines in fish stocks. Human Health Findings: Methylmercury and PCBs are the ocean pollutants whose human health effects are best understood. Exposures of infants in utero to these pollutants through maternal consumption of contaminated seafood can damage developing brains, reduce IQ and increase children’s risks for autism, ADHD and learning disorders. Adult exposures to methylmercury increase risks for cardiovascular disease and dementia. Manufactured chemicals – phthalates, bisphenol A, flame retardants, and perfluorinated chemicals, many of them released into the seas from plastic waste – can disrupt endocrine signaling, reduce male fertility, damage the nervous system, and increase risk of cancer. HABs produce potent toxins that accumulate in fish and shellfish. When ingested, these toxins can cause severe neurological impairment and rapid death. HAB toxins can also become airborne and cause respiratory disease. Pathogenic marine bacteria cause gastrointestinal diseases and deep wound infections. With climate change and increasing pollution, risk is high that Vibrio infections, including cholera, will increase in frequency and extend to new areas. All of the health impacts of ocean pollution fall disproportionately on vulnerable populations in the Global South – environmental injustice on a planetary scale. Conclusions: Ocean pollution is a global problem. It arises from multiple sources and crosses national boundaries. It is the consequence of reckless, shortsighted, and unsustainable exploitation of the earth’s resources. It endangers marine ecosystems. It impedes the production of atmospheric oxygen. Its threats to human health are great and growing, but still incompletely understood. Its economic costs are only beginning to be counted. Ocean pollution can be prevented. Like all forms of pollution, ocean pollution can be controlled by deploying data-driven strategies based on law, policy, technology, and enforcement that target priority pollution sources. Many countries have used these tools to control air and water pollution and are now applying them to ocean pollution. Successes achieved to date demonstrate that broader control is feasible. Heavily polluted harbors have been cleaned, estuaries rejuvenated, and coral reefs restored. Prevention of ocean pollution creates many benefits. It boosts economies, increases tourism, helps restore fisheries, and improves human health and well-being. It advances the Sustainable Development Goals (SDG). These benefits will last for centuries. Recommendations: World leaders who recognize the gravity of ocean pollution, acknowledge its growing dangers, engage civil society and the global public, and take bold, evidence-based action to stop pollution at source will be critical to preventing ocean pollution and safeguarding human health. Prevention of pollution from land-based sources is key. Eliminating coal combustion and banning all uses of mercury will reduce mercury pollution. Bans on single-use plastic and better management of plastic waste reduce plastic pollution. Bans on persistent organic pollutants (POPs) have reduced pollution by PCBs and DDT. Control of industrial discharges, treatment of sewage, and reduced applications of fertilizers have mitigated coastal pollution and are reducing frequency of HABs. National, regional and international marine pollution control programs that are adequately funded and backed by strong enforcement have been shown to be effective. Robust monitoring is essential to track progress. Further interventions that hold great promise include wide-scale transition to renewable fuels; transition to a circular economy that creates little waste and focuses on equity rather than on endless growth; embracing the principles of green chemistry; and building scientific capacity in all countries. Designation of Marine Protected Areas (MPAs) will safeguard critical ecosystems, protect vulnerable fish stocks, and enhance human health and well-being. Creation of MPAs is an important manifestation of national and international commitment to protecting the health of the seas.
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A series of terephthalamides were successfully produced by rapid catalyst-free microwave-assisted aminolysis of polyethylene terephthalate (PET). The produced terephthalamides from chemical recycling of PET were further utilized as reactants for fabrication of plastic films by a radical thiol-ene reaction or they were evaluated as plasticizers for polylactide (PLA). The chemical recycling by aminolysis was performed with four different amines: allylamine, ethanolamine, furfurylamine or hexylamine. The microwave-assisted process led selectively to good yields of well-defined terephthalamides with different terminal functional groups depending on the used amine. The reaction time varied from 10 to 60 min. The end-product obtained after aminolysis with allylamine was further reacted with a thiol through a radical thiol-ene reaction, producing good quality films with glass transition temperature (Tg) above room temperature. The three other terephthalamides were mixed with PLA at 10 wt% and evaluated as plasticizers. The terephthalamide produced by aminolysis with furfurylamine, increased the strain at break 20 times compared to the strain at break of neat PLA. The results illustrate that chemical recycling of PET by aminolysis is a viable and versatile option, producing a library of valuable chemical compounds ready for further use in material applications.
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The rate of acid-base-catalyzed dehydration of alcohols strongly depends on the solvent and the environment of the acid sites. We find that Brønsted acidic sites in large-pore zeolites, but not in medium-pore zeolites, catalyze cyclohexanol dehydration in decalin at significantly higher rates than hydrated hydronium ions in aqueous phase. Specifically, the difference in turnover rates between the two solvents amounts to 2-3 orders of magnitude on H-BEA and H-FAU, while being very modest (within a factor of 2) for H-MFI. Combining kinetic, isotopic tracer, and 2H NMR measurements, it is established that cyclohexanol dehydration generally follows an E1-elimination pathway in decalin. A notable exception is the monomer dehydration route on H-MFI, which exhibits a much lower activation energy and a substantially negative activation entropy that appear to be associated with an E2-type mechanism. The C-O bond cleavage displays a dominant degree of rate control in decalin, which stands in contrast to deprotonation (C-H cleavage) being rate-limiting in aqueous-phase dehydration.
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There is a growing interest in the depolymerization of polyethylene terephthalate (PET) waste for both environmental and economic reasons by chemical methods. In this work, PET waste was depolymerized through aminolysis using excess amount of monoethanolamine. Bis (2-hydroxy ethylene) terephthalamide (BHETA) was obtained as the main product. For the first time, the reaction conversion was calculated, by FTIR, DSC, TGA, and CHN methods, and compared with that of measured by conventional gravimetric method. As a result, TGA and DSC are the suitable methods for calculating the reaction conversion. The gravimetric method does not measure reaction conversion, but correctly measure the yield of reaction.
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Reducing the carbon intensity of plastics production by sourcing sustainable feedstocks while simultaneously enabling effective polymer recycling represents a potential transformation of 21 st century manufacturing. To evaluate technologies that could enable such changes, it is imperative to compare the sustainability of bio-based and/or circular plastic flows to those of incumbent manufacturing paradigms. To that end, we estimate the supply chain energy requirements and greenhouse gas (GHG) emissions associated with US-based plastics consumption. Major commodity polymers, each of which has a global consumption of at least 1 MMT per year, account for an estimated annual 3.2 quadrillion Btutus (quads) of energy and 104 MMTCO 2e of GHG emissions in the US alone. This study serves as a foundation for comparing the supply chain energy requirements and GHG emissions of today’s plastics manufacturing to tomorrow’s disruptive technologies, to inform the development of bio-based plastics and the circular economy for synthetic polymers.
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The accumulation of plastic waste in the environment has prompted the development of new chemical recycling technologies. A recently reported approach employed homogeneous organometallic catalysts for tandem dehydrogenation and olefin cross metathesis to depolymerize polyethylene (PE) feedstocks to a mixture of alkane products. Here, we build on that prior work by developing a fully heterogeneous catalyst system using a physical mixture of SnPt/γ-Al2O3 and Re2O7/γ-Al2O3. This heterogeneous catalyst system produces a distribution of linear alkane products from a model, linear C20 alkane, n-eicosane, and from a linear PE substrate (which is representative of high-density polyethylene), both in an n-pentane solvent. For the PE substrate, a molecular weight decrease of 73% was observed at 200 °C in 15 h. This type of tandem chemistry is an example of an olefin-intermediate process, in which poorly reactive aliphatic substrates are first activated through dehydrogenation and then functionalized or cleaved by a highly-active olefin catalyst. Olefin-intermediate processes like that examined here offer both a selective and versatile means to depolymerize polyolefins at lower severity than traditional pyrolysis or cracking conditions.
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A new low-temperature catalytic upgrading of waste polyolefinic plastics to valuable chemicals such as liquid fuels and waxes by a heterogeneous catalyst is presented. CeO2-supported Ru (Ru/CeO2) acted as an effective and reusable heterogeneous catalyst, showing much higher activity than other metal-supported catalysts in hydrogenolysis of low-density polyethylene, and the catalyst worked even under mild reaction conditions such as low temperature of 473 K and low H2 pressure of 2 MPa, providing liquid fuel (C5-C21) and wax (C22-C45) in 77% and 15% yields (total 92 % yield), respectively. This catalyst was applicable to hydrogenolysis of various low-density polyethylenes, high-density polyethylene, polypropylene to provide the valuable chemicals (liquid fuel + wax) in high yields (83-90%). Furthermore, a commercial plastic bag and waste polyethylenes could be transformed to the valuable chemicals in high yields (91% and 88% yields).
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A new future for polyethylene Most current plastic recycling involves chopping up the waste and repurposing it in materials with less stringent engineering requirements than the original application. Chemical decomposition at the molecular level could, in principle, lead to higher-value products. However, the carbon-carbon bonds in polyethylene, the most common plastic, tend to resist such approaches without exposure to high-pressure hydrogen. F. Zhang et al. now report that a platinum/alumina catalyst can transform waste polyethylene directly into long-chain alkylbenzenes, a feedstock for detergent manufacture, with no need for external hydrogen (see the Perspective by Weckhuysen). Science , this issue p. 437 ; see also p. 400
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Exchange of deuterium (D) for hydrogen (H) on polyolefins enabled by heterogeneous catalysts is a versatile and relatively inexpensive technique to obtain matched pairs of isotopically labeled and unlabeled polymers. A bimetallic ultrawide pore silica-supported platinum-rhenium catalyst (PtRe/SiO2), originally designed for the hydrogenation of polystyrene (PS), can be used as an isotope exchange catalyst with various saturated hydrocarbon polymers, most notably polyethylene (PE). Recently, we discovered that under certain conditions a commercial linear low-density polyethylene (LLDPE) undergoes severe chain degradation during the H/D exchange reaction. In this study, we explored the effects of reacting various polymers on the PtRe/SiO2 catalyst. First, the extent of hydrogenolysis accompanying deuterium exchange was studied under the most severe reaction conditions (1:1 PtRe/SiO2-to-polymer by weight, 170 °C) with four different polymers: narrow-dispersity PS, perfectly linear PE, poly(ethylene-alt-propylene) (PEP), and a commercial LLDPE. PS was fully saturated to yield poly(cyclohexylethylene) (PCHE) without any detectable hydrogenolysis. Among the polyolefins, linear PE showed the least degradation, PEP incurred an intermediate extent of hydrogenolysis, and LLDPE experienced severe chain degradation; at these reaction conditions, the LLDPE was reduced in weight average molecular weight from 120 to under 11 kg/mol. A time-resolved experiment also revealed the exchange of hydrogen for deuterium on LLDPE coincident with hydrogenolysis following initial uptake of the heavy isotope. This loss of deuterium is due to the interaction of the hydrogenous solvent with the catalyst. Subsequently, the H/D exchange reaction conditions were varied to probe the process leading to LLDPE hydrogenolysis. For this purpose, Pt/SiO2 and PtRe/SiO2 catalysts were compared. When using Pt/SiO2, LLDPE maintained its molecular integrity at all catalyst loadings (1:1, 0.2:1, and 0.1:1 catalyst-to-polymer by weight) and reaction temperatures (130 and 170 °C). In the case of PtRe/SiO2, reducing the catalyst loading decreased but did not eliminate hydrogenolysis of LLDPE. Kinetic experiments and microstructural analysis of the hydrogenolysis products implicated a degradation mechanism involving C-C chain scission away from the tertiary carbon associated with the short (C4H9)-chain branches. These findings suggest a degradation mechanism mediated by the cooperative adsorption of the four-carbon side-chain and backbone units on the catalyst surface. The results of this study set important limitations on the conditions that can be employed to exchange deuterium for hydrogen on LLDPE and other polyolefins using the high-surface-area wide pore PtRe/SiO2 heterogeneous catalyst.
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The constant increase of plastic waste released into the environment is a global problem which is of increasing concern to the general population. Although there are many different approaches to the recycling of plastics, chemical recycling is currently seen as one of the most promising technologies in that it allows plastic waste to fit into a sustainable, circular economy. Herein we investigate the chemical recycling of Bisphenol A polycarbonate (BPA-PC) using diols of different chain lengths to yield Bisphenol A and innovative carbonate-containing diols. Subsequently, the latter are polymerised into a series of unique value-added aliphatic polycarbonates (APC). The new polymers obtained by this method have shown promising values of ionic conductivity that make them attractive candidates to be implemented as sustainable polymer electrolytes for solid-state batteries. This procedure opens the way for recycling methods to produce unique, innovative materials using plastic waste as an alternative sustainable feedstock.