Synthetic fibers in atmospheric fallout: A source of microplastics in the environment?

https://doi.org/10.1016/j.marpolbul.2016.01.006Get rights and content

Highlights

  • Atmospheric fallout of fibers is higher at a more urbanized site.

  • 29% of the fibers in atmospheric fallout contain petrochemicals.

  • Atmospheric fallout appears to be an important source of microplastics.

Abstract

Sources, pathways and reservoirs of microplastics, plastic particles smaller than 5 mm, remain poorly documented in an urban context. While some studies pointed out wastewater treatment plants as a potential pathway of microplastics, none have focused on the atmospheric compartment. In this work, the atmospheric fallout of microplastics was investigated in two different urban and sub-urban sites. Microplastics were collected continuously with a stainless steel funnel. Samples were then filtered and observed with a stereomicroscope. Fibers accounted for almost all the microplastics collected. An atmospheric fallout between 2 and 355 particles/m2/day was highlighted. Registered fluxes were systematically higher at the urban than at the sub-urban site. Chemical characterization allowed to estimate at 29% the proportion of these fibers being all synthetic (made with petrochemicals), or a mixture of natural and synthetic material. Extrapolation using weight and volume estimates of the collected fibers, allowed a rough estimation showing that between 3 and 10 tons of fibers are deposited by atmospheric fallout at the scale of the Parisian agglomeration every year (2500 km2). These results could serve the scientific community working on the different sources of microplastic in both continental and marine environments.

Introduction

Microplastics are a widespread particular contaminant originating from the breakdown of larger plastic debris (secondary) or directly manufactured on a millimetric or submilletric size (primary) (Cole et al., 2011). These plastics have been defined as particles with the largest dimension smaller than 5 mm (Arthur et al., 2008); they cover a continuous spectrum of sizes and shapes including 1D-fibers, 2D-fragments and 3D-spheres.

Given their size, these microparticles can be ingested by a wide range of species, either in marine (Anastasopoulou et al., 2013, Lusher et al., 2013, Thompson et al., 2004) or freshwater environments (Sanchez et al., 2014). These microplastics have negative effects on organisms and the possibility of their translocation, bioaccumulation and trophic accumulation is currently being debated (Wright et al., 2013).

While marine plastic pollution has been well documented, there has been limited focus on the continental contamination (Dris et al., 2015b, Wagner et al., 2014). Moreover, its sources, pathways and reservoirs in urban environments remain largely unknown. It is crucial to gather a better knowledge about these particles in the continental environment as rivers are said to be the main source of marine microplastics (Andrady, 2011). If it is very often cited that 80% of the fibers in the marine environment come from the continent, this estimation is not well documented and demonstrated.

Synthetic fibers are one of the forms in which microplastics can be found. They derive presumably from synthetic clothing or macroplastics. Different pathways are thought to be an important source of fibrous microplastics in the aquatic environment. It has been shown that laundry washing machines discharge large amounts of microplastics into wastewaters (reaching 1900 fibers in one wash (Browne et al., 2011)). During wastewater treatment, synthetic fibers are known to contaminate sewage sludge (Habib et al., 1998, Zubris and Richards, 2005). The sources and fate of microplastics in the various compartments of the urban environment are poorly documented (Dris et al., 2015a); this paper focuses on the atmospheric compartment and investigates the contribution of the atmospheric fallout as a potential vector of plastic pollution.

Section snippets

Materials and methods

Total atmospheric fallout was collected on two sampling sites: one in a dense urban environment (48°47′17.8″N, 2°26′36.2″E – Site 1 – Fig. 1) and one in a less dense sub-urban environment. (48°50′27.8″N, 2°35′15.3″E – Site 2 – Fig. 1). Site 1 was monitored over a period of one year (February 19th 2014 to March 12th 2015) and site 2 for a shorter period from October 3rd to 12th March 2015. Site 1 is localized in an area of 7900 inhabitants/km2 while site 2 is characterized by a surrounding

Results and discussion

Based on a long term monitoring (one year), our results show large amounts of fibers in the atmospheric fallout, which has not yet been reported in the literature. Throughout the year of monitoring (site 1), the atmospheric fallout ranged from 2 to 355 particles/m2/day (Fig. 2) with an average atmospheric fallout of 110 ± 96 particles/m2/day (mean ± SD), indicating a high annual variability. On Site 2 (6-month monitoring), the atmospheric fallout was around 53 ± 38 particles/m2/day (mean ± SD).

Fig. 3

Conclusions

These results show a significant amount of fibers in atmospheric fallout, which leads to the hypothesis that the atmospheric compartment should not be neglected as a potential source of microplastics, specially knowing that we estimated at 29%, the amount of these fibers containing at least partially plastic polymers. These microplastics have different possible sources: synthetic fibers from clothes and houses, degradation of macroplastics, and landfills or waste incineration. The

Acknowledgments

We address sincere thanks to the members of the LISA (Laboratoire Interuniversitaire des Systèmes Atmosphériques), especially Anne Chabas. The PhD of Rachid Dris is funded by the region Île-de-France Research Network on Sustainable Development (2013-02) (R2DS Ile-de-France). We thank Kelsey Flanagan for lingual improvements on the manuscript. We thank the members of the ICMPE (Institut de Chimie et des Materiaux Paris-Est) especially Mohamed Guerrouache and Valérie Langlois. We also thank

References (20)

  • A. Anastasopoulou et al.

    Plastic debris ingested by deep-water fish of the Ionian Sea (Eastern Mediterranean)

    Deep Sea Res. Part Oceanogr. Res. Pap.

    (2013)
  • A.L. Andrady

    Microplastics in the marine environment

    Mar. Pollut. Bull.

    (2011)
  • C. Arthur et al.

    Proceedings of the International Research. Presented at the Worshop on the Occurence, Effects and Fate of Microplastic Marine Debris. Sept 9–11 2008

  • M.A. Browne et al.

    Accumulation of microplastic on shorelines woldwide: sources and sinks

    Environ. Sci. Technol.

    (2011)
  • M. Cole et al.

    Microplastics as contaminants in the marine environment: a review

    Mar. Pollut. Bull.

    (2011)
  • R. Dris et al.

    Microplastic contamination in an urban area: a case study in Greater Paris

    Environ. Chem.

    (2015)
  • R. Dris et al.

    Beyond the ocean: contamination of freshwater ecosystems with (micro-) plastic particles

    Environ. Chem.

    (2015)
  • C.M. Free et al.

    High-levels of microplastic pollution in a large, remote, mountain lake

    Mar. Pollut. Bull.

    (2014)
  • F. Galgani et al.

    Marine litter within the European marine strategy framework directive

    ICES J. Mar. Sci.

    (2013)
  • D. Habib et al.

    Synthetic fibers as indicators of municipal sewage sludge, sludge products, and sewage treatment plant effluents

    Water Air Soil Pollut.

    (1998)
There are more references available in the full text version of this article.

Cited by (1351)

  • Airborne microplastics in the roadside and residential areas of Southern Thailand

    2024, Case Studies in Chemical and Environmental Engineering
View all citing articles on Scopus
View full text