Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2021 Aug 6;11(15):9159-9167.
doi: 10.1021/acscatal.1c02133. Epub 2021 Jul 9.

Conversion of Polyethylene Waste into Gaseous Hydrocarbons via Integrated Tandem Chemical-Photo/Electrocatalytic Processes

Affiliations

Conversion of Polyethylene Waste into Gaseous Hydrocarbons via Integrated Tandem Chemical-Photo/Electrocatalytic Processes

Christian M Pichler et al. ACS Catal. .

Abstract

The chemical inertness of polyethylene makes chemical recycling challenging and motivates the development of new catalytic innovations to mitigate polymer waste. Current chemical recycling methods yield a complex mixture of liquid products, which is challenging to utilize in subsequent processes. Here, we present an oxidative depolymerization step utilizing diluted nitric acid to convert polyethylene into organic acids (40% organic acid yield), which can be coupled to a photo- or electrocatalytic decarboxylation reaction to produce hydrocarbons (individual hydrocarbon yields of 3 and 20%, respectively) with H2 and CO2 as gaseous byproducts. The integrated tandem process allows for the direct conversion of polyethylene into gaseous hydrocarbon products with an overall hydrocarbon yield of 1.0% for the oxidative/photocatalytic route and 7.6% for the oxidative/electrolytic route. The product selectivity is tunable with photocatalysis using TiO2 or carbon nitride, yielding alkanes (ethane and propane), whereas electrocatalysis on carbon electrodes produces alkenes (ethylene and propylene). This two-step recycling process of plastics can use sunlight or renewable electricity to convert polyethylene into valuable, easily separable, gaseous platform chemicals.

PubMed Disclaimer

Conflict of interest statement

The authors declare no competing financial interest.

Figures

Scheme 1
Scheme 1. Scheme for Oxidative PE Conversion to Dicarboxylic Acids (a), Which can Subsequently be Converted into Gaseous Hydrocarbon Products via Photocatalysis to Give Alkanes (b) or Electrolysis to Produce Alkenes (c)
Figure 1
Figure 1
Product yields of photocatalytic experiments with (a) P25|Pt and (b) NCNCNx|Pt. Conditions: AM1.5G, 100 mW cm–2, 25 °C, 2 mg mL–1 photocatalyst, and 2 mL of 10 mg mL–1 succinic acid in 0.1 M HNO3 set to pH 4.
Figure 2
Figure 2
(a,b) Product yields from photocatalytic experiments using a flow setup with an irradiated area of 25 cm2 with (a) P25|Pt or (b) NCNCNx|Pt deposited on glass sheets. Conditions: AM1.5G, 100 mW cm–2, backside irradiation, 25 °C, and 50 mL of PE decomposition solution. As the reaction time includes circulation through the reactor and the reservoir, the actual irradiation duration (residence time) is only 0.6 times the reaction time. For each equivalent of hydrocarbon, two equivalents of CO2 are expected to be formed (Figure S5), but the amounts were below the limit of quantification due to the large volume of the reservoir. (c) Photographic image of the photocatalytic flow setup. The PE decomposition solution (not shown in picture) is continuously pumped from a reservoir using a peristaltic pump into the photoreactor (25 cm2 irradiated area) before returning to the reservoir. Evolved gaseous products are sampled and analyzed by GC.
Figure 3
Figure 3
Electrolysis with (a) succinic acid solution, 3.3 mg mL–1, in 0.1 M aqueous HNO3 set to pH 10 by addition of NaOH or in 2:1 methanol/0.1 M aq. HNO3 (set to pH 10 with NaOH) solutions; (b) PE decomposition solution set to pH 10 or 2:1 diluted with methanol. Working electrode: carbon paper (2 cm2 electrode area), counter electrode: Pt foil (2 cm2 electrode area), applied voltage was 5 V until approximately 130 C (= 1 Faradaic equivalent) has been passed through the cell. For each equivalent of hydrocarbon, two equivalents of CO2 are expected to be formed from the decarboxylation reaction (Figure S11).

References

    1. Bauer M.; Lehner M.; Schwabl D.; Flachberger H.; Kranzinger L.; Pomberger R.; Hofer W. Sink–Float Density Separation of Post-Consumer Plastics for Feedstock Recycling. J. Mater. Cycles Waste Manage. 2018, 20, 1781–1791. 10.1007/s10163-018-0748-z. - DOI
    1. Geyer R.; Jambeck J. R.; Law K. L. Production, Use, and Fate of All Plastics Ever Made. Sci. Adv. 2017, 3, e170078210.1126/sciadv.1700782. - DOI - PMC - PubMed
    1. García J. M. Catalyst: Design Challenges for the Future of Plastics Recycling. Chem 2016, 1, 813–815. 10.1016/j.chempr.2016.11.003. - DOI
    1. Vollmer I.; Jenks M. J. F.; Roelands M. C. P.; White R. J.; Harmelen T.; Wild P.; Laan G. P.; Meirer F.; Keurentjes J. T. F.; Weckhuysen B. M. Beyond Mechanical Recycling: Giving New Life to Plastic Waste. Angew. Chem., Int. Ed. 2020, 59, 15402–15423. 10.1002/anie.201915651. - DOI - PMC - PubMed
    1. Lopez G.; Artetxe M.; Amutio M.; Alvarez J.; Bilbao J.; Olazar M. Recent Advances in the Gasification of Waste Plastics. A Critical Overview. Renewable Sustainable Energy Rev. 2018, 82, 576–596. 10.1016/j.rser.2017.09.032. - DOI