Abstract
Plastic pellets (small granules, 1-5 millimeters in diameter) are widely distributed in the ocean
 and coastal zones all over the world. They are an industrial raw material for the plastic
 industry and are unintentionally released to the environment both during manufacturing and
 transport. These pellets are highly persistent and because of their hydrophobic nature they
 have being identified as carriers of toxic chemicals in the marine environment. Several marine
 organisms accumulate plastic particles in their stomach. A positive correlation between the
 mass of ingested plastic and PCBs in fat tissues has been documented. Also, plastic pellets
 are proposed as indicators of organic pollution in the sea. However, the sorption mechanisms
 of organic contaminants onto plastic pellets are not yet well understood. For this reason we
 collected such pellets from various beaches in Lesvos island. Since this material is highly
 heterogeneous we also obtained, from plastic manufacturers, virgin pellets made from
 polyethylene and polypropylene. Phenanthrene was used as the model sorbate. It is a
 compound with high toxicity and abundance in the environment and relatively easy to use in
 the laboratory. Also, there are many publications dealing with phenanthrene sorption onto
 different materials and our results are easily compared with previous research. Batch
 experiments were performed to determine the sorption kinetics of the pellets. Factors under
 investigation included pellet material, degree of pellet erosion, and sorption kinetic behavior.
 All of the five beaches in Lesvos island investigated had plastic pellets on the sand surface.
 All of these plastic pellets were eroded and 2/3 of them had similar appearance to virgin
 polyethylene pellets obtained from plastic manufacturers. Pellet color is not indicative of
 erosion that will lead to varying sorption kinetic behavior. Pellet density could not be used to
 identify pellets sampled from the beach. Apparent sorption coefficient increases with time for
 all pellets investigated. Thus, sorption into plastic pellets is limited by diffusion in the polymer
 phase. 2/3 of the plastic eroded pellets demonstrate sorption kinetics similar to virgin
 polyethylene pellets after 38 days.
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