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Interactions between polystyrene microplastics and marine phytoplankton lead to species-specific hetero-aggregation

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TLDR
The potential for phytoplankton cells and residual organic matter to interact with microplastics, and thus potentially influence their distribution and bioavailability in experimental systems and the water column, is assessed.
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This article is published in Environmental Pollution.The article was published on 2017-09-01 and is currently open access. It has received 242 citations till now. The article focuses on the topics: Microplastics & Phytoplankton.

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Citations
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Journal ArticleDOI

Arctic sea ice is an important temporal sink and means of transport for microplastic

TL;DR: It is shown that MPs in sea-ice have no uniform polymer composition and that, depending on the growth region and drift paths of the sea ice, unique MP patterns can be observed in different sea ice horizons.
Journal ArticleDOI

High Quantities of Microplastic in Arctic Deep-Sea Sediments from the HAUSGARTEN Observatory.

TL;DR: The deep sea as a major sink for microplastics and the presence of accumulation areas in this remote part of the world, fed by plastics transported to the North via the Thermohaline Circulation are corroborated.
Journal ArticleDOI

Ecotoxicological effects of microplastics on biota: a review.

TL;DR: The present review focused on the ecological impact of microplastics on biota at different trophic levels, its uptake, accumulation, and excretion etc., and its plausible mechanistic toxicity with risk assessment approaches.
Journal ArticleDOI

Phytoplankton response to polystyrene microplastics: Perspective from an entire growth period.

TL;DR: It is confirmed that polystyrene microplastics can impair but then enhance algae growth, which will be helpful in understanding the ecological risks of microplastic.
Journal ArticleDOI

Microplastics in the environment: A critical review of current understanding and identification of future research needs

TL;DR: The results reveal that whilst marine microplastics have received substantial scientific research, the extent of microplastic pollution in continental environments, such as rivers, lakes, soil and air, and environmental interactions, remains poorly understood.
References
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Journal ArticleDOI

Plastic waste inputs from land into the ocean

TL;DR: This work combines available data on solid waste with a model that uses population density and economic status to estimate the amount of land-based plastic waste entering the ocean, which is estimated to be 275 million metric tons.
Book ChapterDOI

Culture of Phytoplankton for Feeding Marine Invertebrates

TL;DR: The methods suffice for the most fastidious algae now routinely cultivable, and simplifications indicated for less demanding species are easily made; for example, omission of silicate for plants other than diatoms.
Journal ArticleDOI

Accumulation and fragmentation of plastic debris in global environments.

TL;DR: Global plastics production and the accumulation of plastic waste are documented, showing that trends in mega- and macro-plastic accumulation rates are no longer uniformly increasing and that the average size of plastic particles in the environment seems to be decreasing.
Journal ArticleDOI

Microplastics as contaminants in the marine environment: a review.

TL;DR: Ingestion of microplastics has been demonstrated in a range of marine organisms, a process which may facilitate the transfer of chemical additives or hydrophobic waterborne pollutants to biota.
Related Papers (5)
Frequently Asked Questions (13)
Q1. What have the authors contributed in "Interactions between polystyrene microplastics and marine phytoplankton lead to species-specific hetero-aggregation" ?

However, the behaviour of MP with marine phytoplanktonic cells remains little studied and thus unpredictable. The present study assessed the potential for phytoplankton cells to form hetero-aggregates with small micro-polystyrene ( micro-PS ) particles depending on microalgal species and physiological status. Overall, these results highlight the potential for single phytoplankton cells and residual organic matter to interact with microplastics, and thus potentially influence their distribution and bioavailability in experimental systems and the water column. 

Since EPS/TEP production was not measured here, further studies are needed to confirm the hypothesis linking cell physiology, EPS and the formation of hetero-aggregates with micro-PS. Overall, the variety of MP occurring in the environment is more diverse ( polymer size, type, shape and concentration ) than the spherical MP commonly used in laboratory experiments and this should be adequately addressed in future studies ( Huvet et al., 2016 ). Future directions for field studies Observations of micro-PS adsorbing to suspended cells of C. neogracile and bacterial aggregates suggests that suspended particulate organic matter may influence MP buoyancy and settling in the water column ( and vice versa ), as already suggested for phytoplankton aggregates ( Long et al., 2015 ) and zooplankton faecal pellets ( Cole et al., 2016 ). Further studies moving towards more realistic scenarios ( e. g. natural plankton communities or mesocosm experiments ) are required to evaluate the ecological relevance of phytoplankton/MP hetero-aggregation. 

The fraction of micro-PS stuck to the glassware increased throughout the growth cycle up to 75 ± 4% at the end of the exponential growth phase (day 14), while 22 ± 4% of the remaining micro-PS were suspended and only 3 ± 1% were detected as hetero-aggregates. 

The aim of the present study is to investigate the potential for marine phytoplankton cells to aggregate with micro-PS depending on phytoplankton species and physiological state under experimental conditions. 

Due to confounding factors of MP dose and size in laboratory experiments, conflicting results on MP toxicity exist in the literature. 

the present work highlighted the use of flow cytometry as a promising tool to quantify and characterize small microplastics (<200 µm) in seawater. 

On day 3, no hetero-aggregates were observed and 79 ± 4% of the micro-PS appeared in suspension as free beads or homo-aggregates. 

Micro-PS partitioning in the glass flasks was defined as (i) free suspended beads, (ii) heteroaggregates constituted by micro-PS and microalgal cells and (iii) microbeads adsorbed to the glassware (on the flask walls). 

bacteria and algae can be associated to produce EPS, TEPs, and promote aggregation (Alldredge et al., 1993; Passow, 2002a,b). 

MP distribution in different media (e.g. suspended, floating, adsorbed to experimental containers, trapped in organic aggregates, or adsorbed on or ingested by organisms) must be assessed to obtain accurate values of the actual MP concentration to which the organisms are exposed, as it is commonly done for other pollutant studies. 

Although this study has highlighted a mechanism, the ecological relevance of such laboratory observations is likely low, as they are far from reflecting the complexity of the marine environment (relatively static conditions, small volumes, high algal cell concentrations, one microalgal species, one plastic type, size, dose, etc.). 

To make this possible, technological developments are required to improve MP sampling at sea, especially the fraction consisting of small MP, which may be associated with suspended organic and inorganic materials. 

in stationary growth phase (day 29), the proportion of hetero-aggregates consisting of diatoms and micro-PS reached 19 ± 6%.