Visible light photocatalytic degradation of microplastic residues with zinc oxide nanorods
Microplastics have recently become a major environmental issue due to their ubiquitous distribution, uncontrolled environmental occurrences, small sizes and long lifetimes. Actual remediation methods include filtration, incineration and advanced oxidation processes such as ozonation, but those methods require high energy or generate unwanted by-products. Here we tested the degradation of fragmented, low-density polyethylene (LDPE) microplastic residues, by visible light-induced heterogeneous photocatalysis activated by zinc oxide nanorods. The reaction was monitored using Fourier-transform infrared spectroscopy, dynamic mechanical analyser and optical imaging. Results show a 30% increase of the carbonyl index of residues, and an increase of brittleness accompanied by a large number of wrinkles, cracks and cavities on the surface. The degree of oxidation was directly proportional to the catalyst surface area. A mechanism for polyethylene degradation is proposed.
KeywordsMicroplastic Low-density polyethylene Photocatalysis Zinc oxide Nanotechnology Visible light
Recent studies have shown the ubiquitous distribution of fragmented plastics of sizes less than 5 mm, typically referred to as microplastics, in the biosphere, due to years of improper disposal of plastic materials, mismanagement and negligent littering (Eerkes-Medrano et al. 2015, Van Cauwenberghe et al. 2015, Auta et al. 2017). A small fraction of larger sized plastic materials are recovered, incinerated or recycled for further use. The rest of the plastics end up in landfills, waterways, drainage systems and wastewater plants. Wastewater treatment plants have been identified as one of the major potential sources of microplastics pollution in aquatic systems mainly contributed by consumer plastics, industrial abrasion, air blasting media, cosmetic products, textiles, medicines as well as the breakdown of larger particles (Bergmann et al. 2015; Talvitie et al. 2015). Several studies have suggested advanced treatment technologies for the removal of microplastics from wastewater treatment system (Talvitie et al. 2017). Research is also focusing on the development of sustainable, bio-based plastic polymers (Kuswandi 2017; Brandelli et al. 2017).
Existing approaches for handling waste plastic materials are thermal, catalytic, mechanical, chemical, ozonation and photo-oxidative degradation (Klein et al. 2018); yet studies showed that photocatalysis could be viable, inexpensive and energy efficient for polymer degradation. Photocatalysis is a light-mediated redox process, wherein nanostructured semiconductors excited with appropriate light energy lead to the creation of exciton pairs, which react with surrounding water/moisture to produce highly reactive species like superoxides and hydroxyl radicals that can effectively oxidize organic species including polymers (Ali et al. 2016; Qi et al. 2017; Çolak et al. 2017; Baruah et al. 2016).
Amongst popular metal oxide photocatalysts, ZnO stands out to be the most promising owing to its band gap (3.37 eV), excellent optical properties, high redox potential, better electron mobility and non-toxicity. In addition, ZnO is easy to synthesize and can be formed into different shapes and sizes using facile low-temperature hydrothermal growth processes (Qi et al. 2017; Baruah and Dutta 2009; Çolak et al. 2017). ‘Nano’ sized materials are of great importance due to high surface to volume ratio compared to bulk materials as photocatalysis is a surface-driven phenomenon (Baruah et al. 2016).
In this study, ZnO nanorod photocatalysts were used to degrade LDPE film (residual), which is an abundant microplastic pollutant in wastewater systems (Talvitie et al. 2017). Suitability of photocatalysis as a process to degrade solid phase LDPE residues in water was evaluated and a possible chemical pathway has been proposed.
Materials and methods
Zinc acetate dihydrate [Zn(CH3COO)2, molecular weight: 219.5 g/mol], Zinc nitrate hexahydrate [Zn(NO3)2·6H2O, molecular weight: 297.47 g/mol]and Hexamethylenetetramine [C6H12N4, molecular weight: 140.19 g/mol] were purchased from Sigma-Aldrich. Commercially available, solid LDPE film of 50 µm thicknesses was used for the degradation studies.
Growth of zinc oxide nanorods
Zinc oxide (ZnO) nanorods were hydrothermally grown on glass substrates (Baruah and Dutta 2009). Briefly, a seed ZnO layer was formed by spray pyrolysis of 10 mM Zn(CH3COO)2 at 1 mL/min on clean microscopic glass slides placed on a hot plate at 350 ºC. ZnO nanorods were grown by subsequently placing the seeded substrates in a chemical bath of equimolar solutions of hexamine and zinc nitrate hexahydrate in DI water for 5 h at 90 °C, followed by post-synthesis annealing in air at 350 °C for 1 h.
Experimental set-up for photocatalytic degradation of low-density polyethylene film
Photocatalytic degradation of low-density polyethylene (LDPE) film of size (1 cm × 1 cm) was carried out for 175 h in a petri dish containing the photocatalyst and deionized water. A 50 W dichroic halogen lamp in ambient air was used for visible light illumination (≈ 60–70 klux) from a distance of 10 cm (supporting info. Fig. S1).
Scanning electron microscope (SEM) (ZEISS Ultra 55) was used for the determination of surface morphology and size ranges of catalysts. A digital microscope (Leica: DFC295) fitted with a 3.0 megapixel camera was used for observing the morphological changes over the surface of the exposed LDPE film.
Dynamic mechanical analyser (DMA) was used to determine mechanical changes within the polymer at molecular levels. Both controlled, and pre-stressed LDPE films were exposed to a sinusoidal stress and strain at different temperatures (− 20 ºC to + 100 ºC) at 1 Hz frequency. Storage modulus (Es) that represents the elastic behaviour of polymer was calculated as in Eq. (1).
Fourier-transform infrared (FTIR) spectroscopy (Nicolet is 10: Thermo scientific) was used for the qualitative observation of molecular changes of the functional groups. The effect of photocatalytic oxidation was monitored by determining both carbonyl and vinyl indices; carbonyl index being the ratio of areas under the absorbance peaks at 1712 cm−1 and 1372 cm−1; vinyl index being the ratio of the area under the absorbance of vinyl group at 909 cm−1 to the area under the same reference peak (Ali et al. 2016).
Result and discussion
Morphological variations of photodegraded low-density polyethylene films
It is generally agreed that excitation of the photocatalyst under optimum light energy leads to the formation of hydroxyl radicals, which have a high oxidation capacity for degrading organic pollutants. Hence longer rods, which by virtue of their increased surface area can generate higher number of radicals, lead to a higher degradation of the LDPE film surface. Further evidence of the LDPE oxidation is also provided by DMA analysis.
Surface topography and composition of designed catalysts
Scanning electron microscopy (SEM) micrographs show that the ZnO nanorods were 250 to 1750 nm long varying in width from 34 to 65 nm for the precursor concentrations of 3 mM, 5 mM, 10 mM and 20 mM, leading to increment of total effective surface area to 6.5, 22, 49 and 55 cm2, respectively (supporting info. Fig. S2 and Table S1). This suggests that longer rods have higher effective surface area and could be more effective for microplastics degradation.
Changes in visco-elastic properties of photocatalysed low-density polyethylene films
Temporal changes of chemical properties during photocatalysis of low-density polyethylene films
A closer observation of the vibrational bands (Fig. 3b) leads to a better understanding of the degradation mechanism. The formation of bonded and non-hydrogen-bonded alcohol species was confirmed by the stretching peaks at 3553 cm−1 and 3606 cm−1. Primary (1170 cm−1), secondary (1280–1325 cm−1) and double-bonded (1048 cm−1) peroxide groups were also observed. Fairly broad and clear peaks observed at 1708 cm−1, 1719 cm−1, 1738 cm−1 and 1747 cm−1 that can be assigned to carboxylic acid, ketones, aldehyde and esters belonging to carbonyl groups (Kumanayaka 2010; Socrates 2004). It has been previously suggested that photo-oxidation of ketones results in the formation of unsaturated vinylidene and vinyl groups at 888 cm−1 and 909 cm−1, respectively (Gardette et al. 2013). Interestingly, vinylidene groups seem to form rapidly before decaying and vinyl groups increase simultaneously with the generation of ketones, due to Norrish type II reactions, which is a part of the photocatalytic degradation process.
Photocatalytic degradation indices
Carbonyl index (CI) and vinyl index (VI) of low-density polyethylene (LDPE) films after 175 h exposure to visible light in the presence of different photocatalysts for monitoring the degree of degradation where higher values suggest better oxidation
Control (non-irradiated) LDPE
LDPE + ZnO (3 mM_5 h)
LDPE + ZnO (10 mM_5 h)
LDPE + ZnO (20 mM_5 h)
Proposed degradation mechanism
This study successfully demonstrates the degradation of microplastic fragments, low-density polyethylene film (LDPE) in water using visible light excited heterogeneous ZnO photocatalysts. Photocatalytic LDPE oxidation led to formation of low molecular weight compounds like hydroperoxides, peroxides, carbonyl and unsaturated groups, resulting in increased brittleness along with wrinkles, cracks and cavities on the LDPE surface. Furthermore, catalyst surface area was found to be important towards enhancing the LDPE degradation. The results provide new insights into the use of a clean technology for addressing the global microplastic pollution with reduced by-products.
This article was supported by the CLAIM (Cleaning Litter by developing and Applying Innovative Methods in European Seas) project which receives funding from the European Union's Horizon 2020 research and innovation programme under Grant agreement No 774586. The authors would also like to thank PP Polymer AB and Functional Materials (FNM), Department of Applied Physics, KTH, Sweden for support.
- Briassoulis D (2005) The effects of tensile stress and the agrochemical Vapam on the ageing of low density polyethylene (LDPE) agricultural films. Part I. Mechanical behaviour. Polym Degrad Stab 88:489–503. https://doi.org/10.1016/j.polymdegradstab.2004.11.021 CrossRefGoogle Scholar
- Gardette M, Perthue A, Gardette JL et al (2013) Photo- and thermal-oxidation of polyethylene: comparison of mechanisms and influence of unsaturation content. Polym Degrad Stab 98:2383–2390. https://doi.org/10.1016/j.polymdegradstab.2013.07.017 CrossRefGoogle Scholar
- Klein S, Dimzon IK, Eubeler J et al (2018) Analysis, occurrence, and degradation of microplastics in the aqueous environment. In: Wagner M, S L (eds) Freshwater microplastics. The handbook of environmental chemistry. Springer, ChamGoogle Scholar
- Kumanayaka TO (2010) Photo-oxidation and biodegradation of polyethylene nanocomposites. Dessertation, RMIT UniversityGoogle Scholar
- Liang W, Luo Y, Song S et al (2013) High photocatalytic degradation activity of polyethylene containing polyacrylamide grafted TiO2. Polym Degrad Stab 98:1754–1761. https://doi.org/10.1016/j.polymdegradstab.2013.05.027 CrossRefGoogle Scholar
- Socrates G (2004) Infrared and Raman characteristic group frequencies: tables and charts, 3rd ed. Wiley, New YorkGoogle Scholar
Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.