Colonisation of plastic pellets (nurdles) by E. coli at public bathing beaches
Introduction
The most abundant form of litter in the marine environment is plastic, which due to its buoyant and persistent characteristics can provide an ideal environment for the formation of biofilm by opportunistic microbial colonisers. The interface between the plastic surface and the environment has been termed the ‘Plastisphere’ (Zettler et al., 2013), and such biofilm formation on marine plastics could provide plastisphere communities with a niche for protection from harmful UV irradiance and predation.
One of the most common types of plastic in the marine environment are virgin plastic resin pellets (or nurdles), a disc shaped plastic particle, typically 3–5 mm diameter, used as the raw material in the production of many thermally moulded plastic products. Nurdles can be accidentally released into the environment, and commonly enter marine systems through ship spills, road runoff, inland waterways, or wind transfer (Boucher and Friot, 2017). Once in the marine environment, nurdles can be deposited in coastal areas via winds, surface currents, and tides (Karkanorachaki et al., 2018), with the potential to be dispersed over long distances (Karlsson et al., 2018). Therefore, nurdles could act as a significant vector for hitchhiking microbes, and facilitate subsequent transport to beaches, bathing waters and shellfish harvesting waters (Keswani et al., 2016).
In Europe, the Bathing Water Directive (BWD), 2006/7/EC, uses faecal indicator organisms (FIOs), such as Escherichia coli, as the key monitoring parameter for regulating compliance of microbial water quality. However, whilst plastic litter in bathing water can influence the survival of E. coli (Quilliam et al., 2014), its ability to bind to, and persist in, the plastisphere of marine plastic debris is currently unknown. Thus, an improved understanding of the potential for nurdles to facilitate the survival of FIOs and human microbial pathogens (e.g. species of Vibrio), and thus increase human exposure routes by providing a vehicle for dispersal around coastal waters, is clearly an area of marine environmental pollution research that needs urgent investigation. Therefore, the aim of this study was to test the hypothesis that nurdles deposited on bathing beaches can act as a vector for E. coli persistence at public bathing beaches.
Section snippets
Methods
Nurdles were collected from five EU designated bathing beaches (Fig. 1) situated on the Forth Estuary (East Lothian, Scotland, UK), which are approximately 45 km downstream of the industrial town of Grangemouth, and 30 km downstream from the large urban settlement of Edinburgh. North Berwick (Milsey Bay) is the only sampling site in which the bathing water catchment contains both rural and urban land uses; the other four sites are all predominantly rural catchments. Waste water treatment works
Results and discussion
Plastic nurdles were found at all five public bathing beaches, and were distributed heterogeneously on the sand along the high tide mark (Fig. 2). At each beach, the highest densities of nurdles were found in discrete areas either behind rocks or amongst organic debris and detached seaweeds. The presence of detached seaweed and other debris in these areas may facilitate the settlement of buoyant plastics as the tide goes out (Turner and Holmes, 2011). The direction of prevailing winds and major
Conclusion
There is currently a significant lack of data on the negative implications of marine plastics capable of supporting diverse microbial communities and potentially disseminating FIOs and/or pathogenic microorganisms within the marine and coastal environment. The potential for the wider global dissemination of FIOs and human pathogens by marine plastic debris vectors is further exacerbated by future climate change scenarios, in particular the projected increases in surface water temperature, which
Acknowledgements
This study provided the preliminary data for the project, “Microbial hitch-hikers of marine plastics: the survival, persistence & ecology of microbial communities in the ‘Plastisphere’ (NE/S005196/1)” funded by the UK Natural Environment Research Council (NERC).
References (15)
- et al.
Surface properties of beached plastic pellets
Mar. Environ. Res.
(2012) - et al.
Plastic pellets, meso- and microplastics on the coastline of northern Crete: distribution and organic pollution
Mar. Pollut. Bull.
(2018) - et al.
The unaccountability case of plastic pellet pollution
Mar. Pollut. Bull.
(2018) - et al.
Microbial hitchhikers on marine plastic debris: human exposure risks at bathing waters and beach environments
Mar. Environ. Res.
(2016) - et al.
Dangerous hitchhikers? Evidence for potentially pathogenic Vibrio spp. on microplastic particles
Mar. Environ. Res.
(2016) - et al.
Mature biofilm communities on synthetic polymers in seawater - specific or general?
Mar. Environ. Res.
(2018) - et al.
Seaweeds and plastic debris can influence the survival of faecal indicator organisms in beach environments
Mar. Pollut. Bull.
(2014)
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