Our socioeconomic development models have led to an increased production of consumer goods of every type, facilitated by the petrochemical industry's ability to provide a range of cheap materials that are continuously becoming more varied. Introduced in the 1950s, plastics have continued to evolve for many purposes, and are currently used in all industrial sectors. A noteworthy application is packaging, which currently uses around 30–40% of the exponentially growing annual plastic production.
Plastics are a diverse group of synthetic materials composed of polymers (from the Greek poly = many, and meros = parts) predominantly derived from petrochemicals, such as petroleum and natural gas. Polyethylene, polypropylene, polystyrene, polycarbonates and polyamides, are all plastics manufactured from monomers with different chemical characteristics. They possess different properties (color, form, hardness, thickness, and degradability), which impart various fates once discarded in the environment. Unfortunately, some of the main plastic qualities sought by industry and consumers—lightness and resistance to degradation—are also leading to their negative impacts and persistence in natural habitats.
Marine litter is any directly or indirectly manufactured item thrown or abandoned voluntarily or involuntarily into the marine environment. It is well known that plastic is the main contributor to the growing amounts of litter accumulating in the world's oceans. Nonetheless, the marine plastic pollution research field is quite new, and more information about the nature, sources, transport, distribution and environmental effects of plastics is necessary for a better understanding of their biogeochemical cycles. Various studies have reported the existence of small plastic particles in pelagic and benthic environments that are often invisible to the naked eye. They are commonly referred to as “microplastics” (<5 mm) and can either be microparticles already manufactured in such small sizes or, more commonly, result from the fragmentation of larger plastic objects. The environmental implications of their presence at sea are still largely unknown.
Identifying sources and sinks of marine plastics can be difficult because pollution sources on land and at sea are often unknown and plastic particle transport and aging processes are highly dynamic and complex. Nonetheless, recent research suggest major sources are coastlines, rivers (Lebreton et al., 2017), and maritime (e.g., fishing) activities, with the presence of plastic accumulation zones being present in seafloor environments (Pham et al., 2014), beaches (Lavers and Bond, 2017), and surface waters of subtropical (Eriksen et al., 2014), Mediterranean (Cozar et al., 2015) and Arctic waters (Cozar et al., 2017). Over the past 15 years, plastic impacts in the seas have increased (Galgani, 2014), and the number of marine species known to be affected by this contaminant has gone from 247 to 680 (Gall and Thompson, 2015). A substantial portion of these impacts involves entanglement in fishing equipment and ingestion of debris, and occurs mainly in developing regions. The interaction of litter with marine organisms has been used as an approach to better map some of the risks (Wilcox et al., 2015; Darmon et al., 2017). The alteration of ecosystems caused by the transport of species over long distances also represents a major problem.
Although there is mounting evidence that plastic pollution act as an important stressor for many marine organisms, we do not know how this is affecting the overall functioning of marine ecosystems and the services they provide. This research topic contributes to a better understanding of this type of marine contamination by presenting articles reporting observations and transport models of debris in the Adriatic Sea, Western Australian waters, Great Lakes, North West European seas, and Aegean Sea. There are also studies describing findings from (1) a statistical model that predicts areas of plastic accumulation in the Mediterranean, (2) a 6 months experiment that simulates the generation of microplastics from the fragmentation of Polyethylene films on beaches and at sea, (3) a review of transport models for marine plastics, and (4) models predicting the overlap between fin whales and plastic debris in a marine protected area.
Statements
Author contributions
All authors listed have made a substantial, direct and intellectual contribution to the work, and approved it for publication.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
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Summary
Keywords
plastic, pollution, models, microplastics, degradation
Citation
Galgani F, Pham CK and Reisser J (2017) Editorial: Plastic Pollution. Front. Mar. Sci. 4:307. doi: 10.3389/fmars.2017.00307
Received
12 July 2017
Accepted
07 September 2017
Published
22 September 2017
Volume
4 - 2017
Edited by
Hans Uwe Dahms, Kaohsiung Medical University, Taiwan
Reviewed by
Xiaoshou Liu, Ocean University of China, China; Rodrigo Riera, Atlantic Environmental Marine Center (CIMA SL), Spain
Updates
Copyright
© 2017 Galgani, Pham and Reisser.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) or licensor are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: François Galgani Francois.Galgani@ifremer.fr
This article was submitted to Marine Pollution, a section of the journal Frontiers in Marine Science
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