Quantification of selected microplastics in Australian urban road dust
Zenodo (CERN European Organization for Nuclear Research)2022
Score: 35
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Francisca Ribeiro,
Stacey O’Brien,
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Stacey O’Brien,
Stacey O’Brien,
Francisca Ribeiro,
Tania Toapanta,
Francisca Ribeiro,
Stacey O’Brien,
Stacey O’Brien,
Francisca Ribeiro,
Elvis D. Okoffo,
Stephen D. Burrows,
Stephen D. Burrows,
Francisca Ribeiro,
Francisca Ribeiro,
Francisca Ribeiro,
Elvis D. Okoffo,
Xianyu Wang,
Elvis D. Okoffo,
Elvis D. Okoffo,
Jake O’Brien,
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Francisca Ribeiro,
Elvis D. Okoffo,
Francisca Ribeiro,
Elvis D. Okoffo,
Elvis D. Okoffo,
Stacey O’Brien,
Stacey O’Brien,
Elvis D. Okoffo,
Kevin V. Thomas
Elvis D. Okoffo,
Kevin V. Thomas
Elvis D. Okoffo,
Kevin V. Thomas
Kevin V. Thomas
Elvis D. Okoffo,
Elvis D. Okoffo,
Stacey O’Brien,
Kevin V. Thomas
Kevin V. Thomas
Elvis D. Okoffo,
Kevin V. Thomas
Kevin V. Thomas
Stacey O’Brien,
Kevin V. Thomas
Kevin V. Thomas
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Cassandra Raeurt,
Cassandra Raeurt,
Jake O’Brien,
Jake O’Brien,
Jake O’Brien,
Jake O’Brien,
Francisca Ribeiro,
Francisca Ribeiro,
Francisca Ribeiro,
Francisca Ribeiro,
Tania Toapanta,
Kevin V. Thomas
Kevin V. Thomas
Jake O’Brien,
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Elvis D. Okoffo,
Elvis D. Okoffo,
Elvis D. Okoffo,
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Stacey O’Brien,
Stacey O’Brien,
Stacey O’Brien,
Francisca Ribeiro,
Francisca Ribeiro,
Stephen D. Burrows,
Jake O’Brien,
Jake O’Brien,
Jake O’Brien,
Jake O’Brien,
Francisca Ribeiro,
Elvis D. Okoffo,
Elvis D. Okoffo,
Tania Toapanta,
Elvis D. Okoffo,
Elvis D. Okoffo,
Tania Toapanta,
Elvis D. Okoffo,
Stephen D. Burrows,
Xianyu Wang,
Kevin V. Thomas
Stacey O’Brien,
Kevin V. Thomas
Xianyu Wang,
Stephen D. Burrows,
Elvis D. Okoffo,
Elvis D. Okoffo,
Kevin V. Thomas
Francisca Ribeiro,
Kevin V. Thomas
Elvis D. Okoffo,
Jake O’Brien,
Kevin V. Thomas
Francisca Ribeiro,
Francisca Ribeiro,
Stephen D. Burrows,
Kevin V. Thomas
Kevin V. Thomas
Tania Toapanta,
Kevin V. Thomas
Stephen D. Burrows,
Elvis D. Okoffo,
Tania Toapanta,
Jake O’Brien,
Stacey O’Brien,
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Elvis D. Okoffo,
Kevin V. Thomas
Elvis D. Okoffo,
Kevin V. Thomas
Xianyu Wang,
Tania Toapanta,
Cassandra Raeurt,
Kevin V. Thomas
Xianyu Wang,
Tania Toapanta,
Xianyu Wang,
Xianyu Wang,
Kevin V. Thomas
Cassandra Raeurt,
Xianyu Wang,
Kevin V. Thomas
Kevin V. Thomas
Tania Toapanta,
Tania Toapanta,
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Francisca Ribeiro,
Francisca Ribeiro,
Francisca Ribeiro,
Francisca Ribeiro,
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Kevin V. Thomas
Elvis D. Okoffo,
Elvis D. Okoffo,
Kevin V. Thomas
Jake O’Brien,
Elvis D. Okoffo,
Kevin V. Thomas
Summary
Researchers quantified microplastics in road dust along an urban-to-rural transect in Southeast Queensland, Australia, using Accelerated Solvent Extraction followed by pyrolysis GC-MS to measure six polymer types across five size fractions. Concentrations ranged from 0.5 mg/g in rural areas to 6 mg/g in Brisbane city, with PVC and PET dominating and the sub-250 µm fraction containing the majority of mass, and vehicle volume explaining 63% of the variance in microplastic concentration.
Microplastics (1 - 5000 µm) are pervasive in every compartment of our environment. However, little is understood regarding the concentration and size distribution of microplastics in road dust, and how they change in relation to human activity. Within road dust, microplastics move through the environment via atmospheric transportation and stormwater run-off into waterways. Human exposure pathways to road dust include dermal contact, inhalation and ingestion. In this study, road dust along an urban to rural transect within South-East Queensland, Australia was analysed using Accelerated Solvent Extraction followed by pyrolysis Gas Chromatography-Mass Spectrometry (Pyr-GC/MS). Polypropylene, polystyrene, polyethylene terephthalate, polyvinyl chloride, poly (methyl methacrylate) and polyethylene were quantified. Microplastic concentrations ranged from 0.5 mg/g (rural site) to 6 mg/g (Brisbane city), consisting primarily of polyvinyl chloride (29%) and polyethylene terephthalate (29%). Size fractionation (¡ 250 µm, 250-500 µm, 500-1000 µm, 1000-2000 µm and 2000-5000 µm) established that the ¡ 250 µm size fraction contained the majority of microplastics by mass (mg/g). Microplastic concentrations in road dust demonstrated a significant relationship with the volume of vehicles (r2 = 0.63), suggesting traffic, as a proxy for human movement, is associated with increased microplastic concentrations in the built environment. Also see: https://micro2022.sciencesconf.org/426553/document