-Coccolithophores. A, Coronosphaera mediterranea HOL (formerly "Calyptrolithina wettsteinii"); B, Calcidiscus leptoporus; C, Zygosphaera hellenica; D, Syracosphaera pulchra; E, Syracosphaera molischii; F, Syracosphaera halldalii; G, Helicosphaera carteri HOL (for. "Syracolithus confusus"); H, Helicosphaera carteri HOL (for. "Syracolithus catilliferus"); I, Umbilicosphaera sibogae; J, Holococcosphaera dentate (for. "Calyptrosphaera"); K, Coccoliths of Emiliania huxleyi on sediment; L, Rhabdosphaera clavigera. 

-Coccolithophores. A, Coronosphaera mediterranea HOL (formerly "Calyptrolithina wettsteinii"); B, Calcidiscus leptoporus; C, Zygosphaera hellenica; D, Syracosphaera pulchra; E, Syracosphaera molischii; F, Syracosphaera halldalii; G, Helicosphaera carteri HOL (for. "Syracolithus confusus"); H, Helicosphaera carteri HOL (for. "Syracolithus catilliferus"); I, Umbilicosphaera sibogae; J, Holococcosphaera dentate (for. "Calyptrosphaera"); K, Coccoliths of Emiliania huxleyi on sediment; L, Rhabdosphaera clavigera. 

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The present study used scanning electron microscopy to characterize the organisms colonizing marine plastic debris collected from pelagic and benthic habitats across Mediterranean coastal waters of Greece, Italy and Spain. A total of 42 fragments of plastic were collected during the COMSOM experimental cruise, 16 from the seafloor and 26 from surfa...

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... analysis of pelagic and benthic plastics us- ing a scanning electron microscope evidenced that the frequencies of eight large groups of coloniz- ers qualitatively differentiated surface and seabed MPD microfouling communities (Table 1). Diatoms (Fig. 2) appeared in almost 100% of both benthic and pelagic MPD sampled. Dinoflagellates (Fig. 3) occurred in more than 50% of the pelagic MPD sampled, but rarely (13%) on benthic MPD. Cocco- lithophores (Fig. 4) were attached on both benthic and pelagic MPD, occurring with a relatively high frequency (Table 1). Fungi were the second group in frequency of appearance (Fig. 5L) on pelagic MPD, but this group only appeared sporadically on benthic MPD. Faecal pellets were detected in both domains although they were more frequently recorded on pe- lagic MPD. Benthic and pelagic MPD had a very distinct appear- ance. Pelagic MPD was characterized, in most cases, by a well-developed biofilm containing a high amount of bacteria, fungi and diatoms (Fig. 5M). Bacteria were present in all analysed samples from both pelagic (Fig. 5A, B, C) and benthic MPD. However, benthic MPD was covered by sediment, basically clay (Fig. 6A, C), which complicated identification of organisms. Benthic MPD was characterized by high quantities of sessile and pedunculated protozoans (Fig. 6A, B, C, D), as well as bryozoan colonies (Fig. 6H) (Table 1). Polychaetes (Fig. 6G) were also identified with a moderate frequency and different species of hydrozoans were detected sporadi- cally in both pelagic (Fig. 5D, E, F) and benthic MPD (Fig. 6E). Foraminifera were also identified in several communities (Fig. 6I) from benthic ...
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... were identified on both pelagic and benthic MPD (Table 1) but coccospheres appeared only on pelagic MPD (Fig. 4A, B, C, D, G), while indi- vidual coccoliths were relatively abundant on benthic MPD. Emiliania huxleyi was the most abundant spe- cies on benthic and pelagic MPD, where it appeared in large quantities (Fig. 4K). Several species of Syra- cosphaera (S. pulchra, S. halldalii, S. molischii) (Fig. 4D, E, F) were highly frequent on pelagic MPD. Addi- tional species identified on pelagic plastics were Syra- colithus confusus, Calcidiscus leptoporus, Corono- sphaera mediterranea HOL (formerly, Calyptrolithina Other biological structures such as eggs and jel- lyfish nematocysts were identified attached to pe- lagic MPD (Fig. 5G, H, I). Pollen grains appeared in some samples in great numbers. Different remains or pieces of copepods or other crustaceans were com- mon organic structures. However, the presence of unidentified organisms or structures was very com- mon (Fig. 5N, ...
Context 3
... were identified on both pelagic and benthic MPD (Table 1) but coccospheres appeared only on pelagic MPD (Fig. 4A, B, C, D, G), while indi- vidual coccoliths were relatively abundant on benthic MPD. Emiliania huxleyi was the most abundant spe- cies on benthic and pelagic MPD, where it appeared in large quantities (Fig. 4K). Several species of Syra- cosphaera (S. pulchra, S. halldalii, S. molischii) (Fig. 4D, E, F) were highly frequent on pelagic MPD. Addi- tional species identified on pelagic plastics were Syra- colithus confusus, Calcidiscus leptoporus, Corono- sphaera mediterranea HOL (formerly, Calyptrolithina Other biological structures such as eggs and jel- lyfish nematocysts were identified attached to pe- lagic MPD (Fig. 5G, H, I). Pollen grains appeared in some samples in great numbers. Different remains or pieces of copepods or other crustaceans were com- mon organic structures. However, the presence of unidentified organisms or structures was very com- mon (Fig. 5N, ...
Context 4
... were identified on both pelagic and benthic MPD (Table 1) but coccospheres appeared only on pelagic MPD (Fig. 4A, B, C, D, G), while indi- vidual coccoliths were relatively abundant on benthic MPD. Emiliania huxleyi was the most abundant spe- cies on benthic and pelagic MPD, where it appeared in large quantities (Fig. 4K). Several species of Syra- cosphaera (S. pulchra, S. halldalii, S. molischii) (Fig. 4D, E, F) were highly frequent on pelagic MPD. Addi- tional species identified on pelagic plastics were Syra- colithus confusus, Calcidiscus leptoporus, Corono- sphaera mediterranea HOL (formerly, Calyptrolithina Other biological structures such as eggs and jel- lyfish nematocysts were identified attached to pe- lagic MPD (Fig. 5G, H, I). Pollen grains appeared in some samples in great numbers. Different remains or pieces of copepods or other crustaceans were com- mon organic structures. However, the presence of unidentified organisms or structures was very com- mon (Fig. 5N, ...

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... Microscopy observations indicated that freshwater eukaryotic microbes of various trophic levels may represent a significant portion of plastisphere biodiversity (Carson et al., 2013;Oberbeckmann et al., 2014;Bryant et al., 2016;Masó et al., 2016), although high-throughput sequencing data are still limited (Kettner et al., 2017;Bhagwat et al., 2021;González-Pleiter et al., 2021;Li et al., 2021;Wang et al., 2021;Weig et al., 2021;Xue et al., 2021;Chaudhary et al., 2022;Di Pippo et al., 2022;Martínez-Campos et al., 2023;Miao et al., 2023;Song et al., 2023;Xu et al., 2024;Zhang et al., 2024). Different taxa of primary producers (Chlorophyta, Charophyta, Bacillariophyta), primary/secondary consumers (Peritrichia, Oligotrichia), mixotrophs (Dinophyceaea), saprotrophic/parasitic Frontiers in Microbiology 10 frontiersin.org ...
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... The potential dispersal of harmful microalgae via plastic debris has previously been documented, mainly in the Mediterranean Sea [8][9][10][11][12]. The combination of increasing marine plastic waste in the ocean and harmful microalgae dispersal could pose a severe threat to our marine ecosystem. ...
... Previous studies have reported that long-distance transport of various microalgae species could naturally be accommodated through floating seaweeds, seagrasses, and detritus [31], migratory birds [32], or airborne [33]. On the other hand, anthropogenic-mediated transports of harmful microalgae via ship ballast water and plastic debris 070001-6 have also been documented [8,12,34,35]. Among possible consequences of their dispersal through plastic garbage and biological debris are the wider distribution range and higher prevalence in coastal waters. ...
... Others produce mucous-like substance that protect the cells while also assist their adhesion to their substrates. The production of extracellular polymeric substances by archaea and bacteria could also support the occurrence of other microorganisms, including microalgae, in the submerged plastic materials [12]. ...
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... The number of studies documenting the dispersal of NNS on marine debris is steadily increasing (e.g. Marques and Breves, 2015;Masó et al., 2016;Carlton et al., 2017;Gündogdu et al., 2017;Miralles et al., 2018;Rech et al., 2018;De-la-Torre et al., 2021). However, a clear understanding of the scale of the problem, and the underlying processes that drive this phenomenon, is lacking. ...
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