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      Recent advances in photocatalytic degradation of plastics and plastic-derived chemicals

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          Abstract

          Plastic products, used in almost all aspects of daily life because of their low cost, durability, and portability, can be broken down into micro- and nano-scale plastics, thereby increasing the risk of human ingestion.

          Abstract

          Plastic products, used in almost all aspects of daily life because of their low cost, durability, and portability, can be broken down into micro- and nano-scale plastics, thereby increasing the risk of human ingestion. Common plastic additives (polybrominated diphenyl ethers, nonylphenols, phthalic acid esters, etc.) will continue to be released into the environment during the aging and decomposition process, leading to an immeasurable and lasting negative impact on the environment. Recently, photocatalytic technology has been recognized as one of the promising proposals to degrade environmental organic pollutants, including plastics and plastic-derived chemicals. However, there are no systematic reviews on the photocatalytic degradation of plastics and plastic-derived chemicals in the current literature. Herein, the photocatalytic degradation of plastic fragments and major plastic-derived chemicals, including phthalic acid ester plasticizers, nonylphenol antioxidants, bisphenol A plasticizer and brominated flame retardants, is systematically investigated. And we reviewed the process and mechanism of photocatalytic degradation of these pollutants. The outlook section, offering insights into the future directions and prospects of photocatalytic degradation of plastics and plastic-derived chemicals, will be highlighted with the aim of overcoming the present limitations by exploiting more efficient photocatalysts and exploring creative application methods.

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          Most cited references256

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          Electrochemical Photolysis of Water at a Semiconductor Electrode

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            Accumulation and fragmentation of plastic debris in global environments.

            One of the most ubiquitous and long-lasting recent changes to the surface of our planet is the accumulation and fragmentation of plastics. Within just a few decades since mass production of plastic products commenced in the 1950s, plastic debris has accumulated in terrestrial environments, in the open ocean, on shorelines of even the most remote islands and in the deep sea. Annual clean-up operations, costing millions of pounds sterling, are now organized in many countries and on every continent. Here we document global plastics production and the accumulation of plastic waste. While plastics typically constitute approximately 10 per cent of discarded waste, they represent a much greater proportion of the debris accumulating on shorelines. Mega- and macro-plastics have accumulated in the highest densities in the Northern Hemisphere, adjacent to urban centres, in enclosed seas and at water convergences (fronts). We report lower densities on remote island shores, on the continental shelf seabed and the lowest densities (but still a documented presence) in the deep sea and Southern Ocean. The longevity of plastic is estimated to be hundreds to thousands of years, but is likely to be far longer in deep sea and non-surface polar environments. Plastic debris poses considerable threat by choking and starving wildlife, distributing non-native and potentially harmful organisms, absorbing toxic chemicals and degrading to micro-plastics that may subsequently be ingested. Well-established annual surveys on coasts and at sea have shown that trends in mega- and macro-plastic accumulation rates are no longer uniformly increasing: rather stable, increasing and decreasing trends have all been reported. The average size of plastic particles in the environment seems to be decreasing, and the abundance and global distribution of micro-plastic fragments have increased over the last few decades. However, the environmental consequences of such microscopic debris are still poorly understood.
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              Microplastics in the marine environment: a review of the methods used for identification and quantification.

              This review of 68 studies compares the methodologies used for the identification and quantification of microplastics from the marine environment. Three main sampling strategies were identified: selective, volume-reduced, and bulk sampling. Most sediment samples came from sandy beaches at the high tide line, and most seawater samples were taken at the sea surface using neuston nets. Four steps were distinguished during sample processing: density separation, filtration, sieving, and visual sorting of microplastics. Visual sorting was one of the most commonly used methods for the identification of microplastics (using type, shape, degradation stage, and color as criteria). Chemical and physical characteristics (e.g., specific density) were also used. The most reliable method to identify the chemical composition of microplastics is by infrared spectroscopy. Most studies reported that plastic fragments were polyethylene and polypropylene polymers. Units commonly used for abundance estimates are "items per m(2)" for sediment and sea surface studies and "items per m(3)" for water column studies. Mesh size of sieves and filters used during sampling or sample processing influence abundance estimates. Most studies reported two main size ranges of microplastics: (i) 500 μm-5 mm, which are retained by a 500 μm sieve/net, and (ii) 1-500 μm, or fractions thereof that are retained on filters. We recommend that future programs of monitoring continue to distinguish these size fractions, but we suggest standardized sampling procedures which allow the spatiotemporal comparison of microplastic abundance across marine environments.
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                Author and article information

                Contributors
                Journal
                JMCAET
                Journal of Materials Chemistry A
                J. Mater. Chem. A
                Royal Society of Chemistry (RSC)
                2050-7488
                2050-7496
                June 15 2021
                2021
                : 9
                : 23
                : 13402-13441
                Affiliations
                [1 ]College of Environmental Science and Engineering
                [2 ]Key Laboratory of Environmental Biology and Pollution Control
                [3 ]Hunan University
                [4 ]Ministry of Education
                [5 ]Changsha 410082
                [6 ]Key Laboratory of Building Safety and Energy Efficiency
                [7 ]Department of Water Engineering and Science
                [8 ]College of Civil Engineering
                Article
                10.1039/D0TA12465F
                36320515
                028565cc-e588-4721-9e34-39c1ba36d36b
                © 2021

                http://rsc.li/journals-terms-of-use

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