Tuesday, 24 November 2015

Microbes take an easy ride on marine plastics

Global plastic production has accelerated dramatically over the past century to over 250 million tonnes produced per year. Most marine litter originated from land based sources and direct human disposal. Plastics threaten all trophic levels with injuries caused by ingestion, entanglement and by toxins or microbial communities on the plastic surface. In particular, micro-organisms ability to adapt to new niches and provide key ecosystem functions through primary production and nutrient cycling means their presence on plastics could have profound influences on both macro and microbiota.

This study investigates the structure and taxonomic composition of microbial assemblages on plastic fragments in both coastal and offshore Northern European waters in respect to season, geographical location and plastic type. To study of assemblages’ spatial and seasonal variation in the North Sea PET water bottles along with glass slides, for reference, were attached to smart buoys for six weeks during winter, spring and summer. Two research cruises used trawled nets at 41 stations during January and July, 2012 to investigate plastic variation of assemblages on plastics already present in the oceans. Sampling stations encompassed the North Sea, English Channel, Celtic Sea and Bristol Channel. Samples were imaged using SEM and sequenced using PCR and Denaturing Gradient Gel Electrophoresis (DGGE), plastic samples were analysed using Fourier transform infrared spectroscopy (FTIR).

SEM images showed the presence of prokaryotic and eukaryotic growth on plastic debris, eukaryotes were attached by filamentous stalks. There was high variability in community structure and composition in relation to location, season, and polymer type despite some underlying similarities. PET bottle communities showed greatest difference in winter compared to those in spring and summer. A high abundance of Bacteriodetes, Cyanobacteriai, Proteobacteria, and the eukarya Stramenopiles were identified on all bottles. Bacteriodetes, including biofilm constituent Tenacbaculum, were abundant on PET bottles across all seasons and sampling. FTIR analysis did not reveal any difference in the surface structure of the PET bottles, however it is unclear whether this is due to lack of microbial action or because this new technique needs refining. There were clear differences between communities on the exposed PET bottles and the collected open water fragments. DGGE analysis on open water fragments showed Cyanobacteria (predominantly Phormidium and Pseudophormidium) were most dominant across all plastic types and sampling stations.


Through an investigation of multiple types of plastic in various locations over a three season time scale this study has highlighted the variation and hinted at the biodiversity on marine plastics. The majority of microbiota inhabiting marine plastics are commonly found in natural biofilms however the study appears to overlook the less abundant bacteria, which could have novel or harmful effects. Similarities were detected between assemblages on plastic and glass, implying links between natural and plastic biofilm colonisers. Plastic biofilms pose a higher risk to oceans as it floats and migrates within water transporting non-native biota. 

Obeckmann, S., Loeder, M. G. J., Gerdts, G., Osborn, M. (2014) Spatial and seasonal variation in diversity and structure of
microbial biofilms on marine plastics in Northern European
waters. Microbiology Ecology. 90: 478-492. http://onlinelibrary.wiley.com/doi/10.1111/1574-6941.12409/epdf 

2 comments:

  1. Really interesting study, did the paper mention if there were any reasons behind the differences in community structure between winter and spring and summer? Such as certain bacteria present in one season and not in another? And did they use different types of plastic in different sizes/shapes? I'm guessing there are lots of factors that could control the settlement of microbial communities - such as water currents and distance from coast etc. could have an effect. It's interesting that there are similarities between glass and plastic though, which shows some microbes are no affected by the difference in material composition which could be dangerous in the long run as you go up the food chain...

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    1. The study suggested environmental parameters were the main mediators of the variation winter and spring and summer as water analysis detected increased temperatures and lower oxygen concentrations in the summer compared to winter. In winter dominant microbes were different at each site, at the most northerly smart buoy the diatom Syndra spp. dominated. Contrastingly, the two other smart buoys were dominated by bacteria: Tenacibaculum (bacteriodetes) and Thiomicrospira (gammaproteobacteria) respectively. In comparison, spring and summer showed higher diversity, summer was dominated by the brown algae Saccharina and Fucus, diatom Asterionella and Cyanobacteria Stanieria and Pseudomrphium across all sites.
      The work used two experimental techniques: to assess the effects on new plastics they exposed PET bottles, evian water bottles specifically, for 6 weeks of winter, spring and summer then cut them up for sampling. To investigate different types of plastic already in the sea they trawled in sites across the North Sea, English Channel, Celtic Sea and Bristol Channel and collected many different types of plastic in all shapes and sizes.
      They also mentioned the need for longer term experiments investigating factors influencing community structure and composition suggesting they were not confident with the effect of environmental factors. You’re right, like so many other in-situ experiments the variability is huge! I think it would be really interesting to run a longer term experiment investigating the assemblages more closely to assess whether the variability is just characteristic of the year of study or of all years.

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