Emissions of microplastic fibers from microfiber fleece during domestic washing
- First Online:
- 2.1k Downloads
Microplastics are found in marine and freshwater environments; however, their specific sources are not yet well understood. Understanding sources will be of key importance in efforts to reduce emissions into the environment. We examined the emissions of microfibers from domestic washing of a new microfiber polyester fleece textile. Analyzing released fibers collected with a 200 μm filter during 10 mild, successive washing cycles showed that emission initially decreased and then stabilized at approx. 0.0012 wt%. This value is our estimation for the long-term release of fibers during each washing. Use of detergent and softener did not significantly influence emission. Release of fibers during tumble drying was approx. 3.5 times higher than during washing.
KeywordsTextile Fiber Microplastics Washing Pollution Polyethylene terephthalate
Plastics were first noticed in oceans in the 1970s (Buchanan 1971; Carpenter et al. 1972; Carpenter and Smith 1972) when plastic production was still far below current levels. More recently, attention of the wider public was caught by the discovery of the north Pacific gyre “garbage patch” by Charles Moore (Moore and Phillips 2012). In the last decade, microplastics (MP), plastic particles smaller than 5 mm (Andrady 2011; Ivar do Sul and Costa 2014), have been gaining attention (Law and Thompson 2014) and a rapidly increasing body of research is now available showing that MP are found in all strata of the marine environment as well as in freshwater environments (Dris et al. 2015; Klein et al. 2015; Gallagher et al. 2015) and even in foodstuffs (Liebezeit and Liebezeit 2013, 2014).
MP are of similar sizes as plankton and can be easily ingested by organisms (Wright et al. 2013). The chemical structure of plastics supports adsorption of non-polar persistent organic pollutants (POPs) (Hirai et al. 2011; Rochman et al. 2013), and the effect is augmented by the increase of the surface-to-volume ratio with decreasing particle sizes. When MP are ingested, the leaching of adsorbed pollutants and additives could be a source of toxic substances influencing the organisms and entering into the food web leading all the way to humans (Koelmans et al. 2013; Rochman et al. 2013; Van Cauwenberghe and Janssen 2014; Rochman et al. 2015).
Sources of MP are known only generally as follows: they emerge from direct use of small particles (primary MP) or from fragmentation of larger plastic debris (secondary MP). Thompson et al. (2004) reported that microfiber concentrations in historical sea-surface water samples correlated with the production volume of synthetic fibers in manufacturing. A prioritization of sources by Verschoor et al. (2014) put a high (7/10) score to textiles and garments made from synthetic materials, which shed fibers during washing and use. In the past, degradation of textiles was studied to understand the limits on useful fabric life (Slater 1986) or in forensics (Watt et al. 2005; De Wael 2010) while emissions into the environment were not a concern. Browne et al. (2011) were the first to identify washing as a source of pollution with plastic fibers. They reported, “a single garment can shed more than 1900 fibers per wash and that all garments released more than 100 fibers per liter of effluent;” however, significant information on the textiles used and the experimental methodology is not reported. Dubaish and Liebezeit (2013) reported a release of 0.033–0.039 wt% fibers from a polyester garment per washing although experimental conditions are not given. A study by the Norwegian Environment Agency (Sundt et al. 2014) estimated the annual fiber release from laundries and households in Norway at 100 and 600 t, respectively, however identified the need for better data as an important knowledge gap. A study by Petersson and Roslund (2015) shows that yarn and textile type combined with usage most affect fiber release during washing. Habib et al. (1996) as well as Zubris and Richards (2005) reported synthetic fibers as an indicator of municipal sewage sludge use in soils, indicating fiber presence in wastewaters as well as spreading routes.
The goal of our study was to obtain currently unavailable mass-based data on the release of fibers during washing of a typical textile that would enable an estimate of the cumulative mass of fibers released into the environment from this source. We also studied the effect of washing detergent and softener on the release.
Materials and methods
Textiles used in the experiments were six identical fleece blankets (120 × 70 cm) purchased for the purpose (Supp. Inf. Fig S1). The blankets were bright red in order to facilitate fiber identification. The average blanket weighed 320 g. FTIR (Perkin Elmer, Spectrum One), scanning electron microscopy (SEM, Carl Zeiss supra 35VP), and stereomicroscopy (Leica DMS 1000) were used.
The washing machine used was a brand new front-loading Bosch model Maxx7 VarioPerfect. Using a new machine reduced the problem of contamination by residual fibers in the machine. Detergent Ariel (Procter & Gamble, France) and fabric softener/conditioner Silan (Henkel, Austria), both commercial products were used.
Collection of released fibers was performed by filtering wastewater from the washing machine using an external custom-built filtration setup with a removable stainless steel filter (disk-shaped, 85 mm diameter) with 200 × 200 μm openings (Supp. Inf. Fig S2). The filter with the collected fibers was removed from the setup and air-dried to a constant mass in a dust-free environment prior to weighing. Relative fiber release was calculated as Δm/% = m(f)/mo(b) × 100 where m(f) equals the mass of fibers collected on the filter, and mo(b) signifies the initial blanket mass.
Washing experiments were carried out using the SuperQuick15 program (duration 15 min, temperature 30 °C, spinning 600 rpm). Experiments in which detergent and/or fabric softener was used were carried out with the addition of 10 mL of each in a fashion specified by the appliance producer. Prior to each set of 10 experiments, the empty machine was cleaned by two wash cycles using a more rigorous program (105 min., 60 °C, 1200 rpm). In the first cleaning cycle, 150 g of citric acid was added to the washing compartment. The wastewater from the cleaning cycles was filtered to monitor that the machine was clean. In all cases, the collected residue on the filters was negligible (max. 0.1 mg (0.00034 ‰)). After each washing experiment, the blanket was tumble-dried in a Whirlpool (AWZ865) drying machine at 40 °C for 18 min. Fibers collected on the built-in filter (openings 180 × 180 μm, Supp. Inf. Fig. S3) were weighed.
Results and discussion
Three series of washing experiments were carried out: (1) without additions, (2) with detergent, and (3) with detergent and fabric softener. In each series, two blankets were separately washed and dried 10 times (Supp. Inf. Fig. S5).
Average relative fiber emissions in weight % in 10 consecutive washing/drying experiments of a polyethylene terephthalate microfiber blanket without additives, using detergent, and using detergent and fabric softener. Each value is based on two parallel experiments
Detergent and softener
Average of exp. 8, 9, 10
The wastewater after filtering contained no visible fibers. To verify the efficiency of a filter with relatively large openings (200 μm) relative to fiber thickness (10 μm), we further filtered two samples of effluent water using a paper filter with 2–3-μm pores. The quantity of collected fiber fragments was very low (we estimate a maximum of several % of the released fibers), but we were not able to quantify it due to large volumes and clogging problems. The fragments were mainly in the 20–200 μm range (Supp. Inf. Fig. S7) with very few long fibers (max. approx. 700 μm). These results show that installation (and maintenance) of a relatively simple and robust filter could prevent most of the emissions.
To verify our results, we washed a five-year-old PET fleece jacket. Microfiber release was 0.00111 wt% (no additive), 0.00123 wt% (detergent), and 0.00136 wt% (detergent + softener) giving an average of 0.00123 wt%. This result is in good agreement with our experimental estimate for long-term release obtained with the blankets, confirming it as an acceptable long-term release value.
We attempted to correlate the mass of the fibers released to their number, however found it impossible to separate the intertwined fibers (Supp. Inf. Fig. S8). We were however able to disentangle some fibers; the range of lengths was 0.3–25.0 mm, with an average length of 5.3 mm; however, the average length may be underestimated due to the particular difficulty of disentangling long fibers. A number of released fibers were very lengthy (up to 25 mm) even after several washings, which is most likely a function of the plush fabric. These lengths indicate disentanglement of full-length fibers covering piles on both sides of the fabric (approx. 10 mm each) and the part fixed in the ground textile. Among all inspected fibers, only one filament from the ground textile (2.5 dtex) was observed while all others originated from pile fibers (1 dtex). Using the average fiber length (5.3 mm), a 1-dtex diameter (1 g per 10.000 m), and the 0.0012 wt% release, we can calculate that a 500-g piece of fabric will release 6 mg of fibers or 11.3 × 103 fibers (although this number may be overestimated due to a likely underestimation of the average fiber length).
Although fibers released during spin-drying are not released into the wastewater, we monitored the quantities (Table 1, Supp. Inf. Table S1). Release of fibers during drying was in all cases higher by an approximate factor of 3.5 than the release during washing. The plot of average releases in Fig. 2 indicates that the long-term release value was not yet reached since values continue trending lower. This assumption was confirmed by the results obtained with the old fleece garment, which gave releases of 0.00111, 0.00103, and 0.00123 wt% during the three drying cycles. The average of 0.00112 wt% is significantly lower than the average 0.00394 wt% we obtained with the blanket.
Our results confirm findings of previous studies indicating fiber release during washing and support the numerous reports of synthetic fibers found in natural marine and freshwater habitats (Thompson et al. 2004; Klein et al. 2015; Gallagher et al. 2015) as well as in organisms (Rochman et al. 2015). The estimated number of fibers released in our experiments (even when taking into account a possible overestimation) is significantly higher than the 1900 fibers per garment/washing reported by Browne et al. (2011) but is much lower than predicted by Bruce et al. (2016)—up to 250 × 103 fibers per garment/washing. It is however significant that we used the 1-dtex mass/fiber-length value which we consider appropriate as opposed to Sundt et al. (2014) and Bruce and al. (2016) using the 300-dtex value. Our weight percent release ratios are significantly lower than the 0.039 wt% reported by Dubaish and Liebezeit (2013) and the very broad range (0.007–0.216 wt%) reported by Bruce et al. (2016) for new garments and front-loading washing machines. Bruce et al. (2016) used two filters (333 and 20 μm) which can attribute for only part of the difference as the smaller mesh collected a minor part of the total fiber release. Partially, the very mild washing conditions used in our experiments probably lead to a conservative fiber release estimate. However, the much longer fibers released in our experiments, 5.3 mm compared to 0.7 mm by Bruce et al. (2016) who used fleece jackets, strongly support the conclusions of Petersson and Roslund (2015) who concluded that fabric structure is the most important factor influencing fiber release. As we are still collecting the first sets of fiber release data, we will need to establish in more detail the influence of washing conditions (e.g., temperature, duration, load size) and fabric properties (fiber type and material, fabric structure, etc.) in order to come to more reliable estimates of the quantitative extent of this type of pollution.
A key result of this study is the indication that fibers are emitted throughout the lifetime of the garment. The importance of our estimated 0.0012 wt% of loose fibers released into the wastewater during each washing lies in the cumulative effects. We performed a rough assessment of emissions for a northern climate with the following assumptions: each resident has one polyester blanket (small size 350 g) washed four times a year and one fleece jacket (500 g), washed eight times a year. Based on our results (0.0012 wt% loss per washing), the mass of released fibers corresponds to 4.5 mg for the blanket and 6.5 mg for the jacket resulting in 70 mg of microfibers released annually per person. For Slovenia with just over 2 million inhabitants, this leads to emissions of approximately 144 kg a year. We believe these are conservative estimates since no new items (with an initially higher release) were considered, and the average person is most likely to own more items made of synthetic fibers (sports clothing, gloves, caps, pet items, etc.). Considering a material density of 1.38 g/cm3 and a fiber diameter of 10 μm, we can calculate that this quantity has a surface of 41,700 m2. Although it was already shown that the majority of fibers released during washing is removed in wastewater treatment plants where these are used (Talvitie et al. 2015; Mintenig et al. 2014) and despite PET absorbing lower quantities of POPs than polyolefins (Wright et al. 2013), we nevertheless believe that the large specific surface of microfibers qualifies this form of microplastics as an important class with a notable contribution to the overall problem of pollutants carried by microplastics (Rios et al. 2007).
Results confirm domestic washing of textiles and garments as a constant and widespread source of plastic microfiber emissions into the environment. We estimate that in the case of a long-fiber polyester plush fleece, 0.0012 wt% of loose microfibers is released into wastewaters during every washing. The effect of detergent and fabric softener use is relatively small. The weight-based quantification of emissions should complement published particle-number reports and help in the assessment of cumulative emissions and potential effects. Our results clearly point out that cumulatively large quantities of microplastics are released into the environment from this source.
The authors thank Prof. Elizabeta Tratar Pirc for her support in experimentation and SEM measurements and Mr. Michael Stark for his helpful and constructive comments. Partial support from the DeFishGear IPA Adriatic strategic project 1° str/00010 co-funded by the European Union, Instrument for Pre-Accession Assistance is acknowledged.
Compliance with ethical standards
Conflict of interest
The authors declare that they have no conflict of interest.
- Bruce N, Hartline N, Karba S, Ruff B, Sonar S, Holden P (2016) Microfiber Pollution and the Apparel Industry. University of California Santa Barbara, Bren School of Environmental Science & Management (accessed 19 Aug 2016) http://brenmicroplastics.weebly.com/uploads/5/1/7/0/51702815/bren-patagonia_final_report.pdf)
- Buchanan JB (1971) Pollution by synthetic fibres. Marine Poll Bull 2(23). doi:10.1016/0025-326X(71)90136-6
- Gallagher A, Rees A, Rowe R, Stevens J, Wright P (2015) Microplastics in the Solent estuarine complex, UK: An initial assessment. Marine Poll Bull doi:10.1016/j.marpolbul.2015.04.002
- Hirai H, Takada H, Ogata Y, Yamashita R, Mizukawa K, Saha M, Kwan C, Moore C, Gray H, Laursen D, Zettler ER, Farrington JW, Reddy CM, Peacock EE, Ward MW (2011) Organic micropollutants in marine plastics debris from the open ocean and remote and urban beaches. Marine Poll Bull 62:1683–1692. doi:10.1016/j.marpolbul.2011.06.004 CrossRefGoogle Scholar
- Mintenig S, Int-Veen I, Löder M, Gerdts G (2014) Mikroplastik in ausgewählten Kläranlagen des Olden-burgisch-Ostfriesischen Wasserverbandes (OOWV) in Niedersachsen“ AWI Report, Helgoland, 8. Okt. 2014. http://www.dwa-bayern.de/tl_files/_media/content/PDFs/LV_Bayern/Abschlussbericht_Mikroplastik_in_Klaeranlagen-3.pdf (in German, accessed 12 April 2016)
- Moore C, Phillips C (2012) Plastic Ocean: How a Sea Captain’s Chance Discovery Launched a Determined Quest to Save the Oceans, Avery. ISBN 1583334246Google Scholar
- Petersson H, Roslund S. (2015) Tvättemissionn: En undersökning av polyesterplaggs fiberutsläpp vid hushållstvättning, University of Borås, Sweden, 2015. https://www.diva-portal.org/smash/get/diva2:820491/FULLTEXT01.pdf (in Swedish, accessed 22 June 2016)
- Sundt P, Schulze P-E, Syversen F (2014) Sources of microplastics-pollution to the marine environment, Report no: M-321|2015, Norwegian Environment Agency (Miljødirektoratet) http://www.miljodirektoratet.no/Documents/publikasjoner/M321/M321.pdf (accessed 19 Aug 2016)
- Talvitie J, Heinonen M, Pääkkönen J-P, Vahtera E, Mikola A, Setälä O, Vahala R (2015) Do wastewater treatment plants act as a potential point source of microplastics? Preliminary study in the coastal Gulf of Finland, Baltic Sea. Water Sci Technol 72:1495–1504. doi:10.2166/wst.2015.360 CrossRefGoogle Scholar
- Verschoor AJ, de Porter L, Roex, E (2014) Quick Scan and Prioritization of Microplastic Sources and Emissions, RIVM Advisory Letter 250012001, National Institute for Public Health and Environment, Bilthoven, The Netherlands. http://www.rivm.nl/dsresource?objectid=rivmp:268299&type=org&disposition=inline&ns_nc=1 (accessed 22 June 2016)
Open Access This 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.