Quantification of toxic metals derived from macroplastic litter on Ookushi Beach, Japan.

The potential risk of toxic metals that could leach into a beach environment from plastic litter washed ashore on Ookushi Beach, Goto Islands, Japan was estimated by balloon aerial photography, in situ beach surveys, and leaching experiments in conjunction with a Fickian diffusion model analysis. Chromium (Cr), cadmium (Cd), tin (Sn), antimony (Sb), and lead (Pb) were detected in plastic litter collected during the beach surveys. Polyvinyl chloride (PVC) fishing floats contained the highest quantity of Pb. Balloon aerial photography in conjunction with a beach survey gave an estimated mass of Pb derived from plastic litter of 313 ± 247 g. Lead leaching experiments on collected PVC floats showed that Pb in the plastic litter could leach into surrounding water on the actual beach, and that plastic litter may act as a "transport vector" of toxic metals to the beach environment. Using the experimental data, the total mass of Pb that could leach from PVC plastic litter over a year onto Ookushi Beach was estimated as 0.6 ± 0.6 g/year, suggesting that toxic metals derived from plastic beach litter are a potential "pathway" to contamination of the beach environment due to their accumulation in beach soil over time.

The potential of oceanic transport and onshore leaching of additive-derived lead by marine macro-plastic debris.

The long-distance transport potential of toxic lead (Pb) by plastic marine debris was examined by pure water leaching experiments using plastic fishery floats containing high level of additive-Pb such as 5100±74.3mgkg(-1). The leaching of Pb ended after sequential 480-h leaching experiments, and the total leaching amount is equivalent to approximately 0.1% of total Pb in a float. But it recovered when the float was scratched using sandpaper. We propose that a "low-Pb layer," in which Pb concentration is negligibly small, be generated on the float surface by the initial leaching process. Thickness of the layer is estimated at 2.5±1.2µm, much shallower than flaws on floats scratched by sandpaper and floats littering beaches. The result suggests that the low-Pb layer is broken by physical abrasion when floats are washed ashore, and that Pb inside the floats can thereafter leach into beaches.

Selective transport of microplastics and mesoplastics by drifting in coastal waters.

The quantity and size distributions of small plastic fragments in the Seto Inland Sea, Japan were investigated using field surveys and a numerical particle-tracking model. The model was used to interpret the distributions of small plastic fragments and the possible transport processes in coastal waters. Of note, the size and quantity of mesoplastics (approximately >5mm) gradually increased close to the coast irrespective of the existence of river mouths, which probably act as a major source of anthropogenic marine debris. Additionally, microplastics were more dominant as we moved further offshore. The numerical model reproduced the near-shore trapping of mesoplastics, suggesting that mesoplastics are selectively conveyed onshore by a combination of Stokes drift and terminal velocity, dependent on fragment sizes. It is suggested that mesoplastics washed ashore on beaches degrade into microplastics, and that the microplastics, which are free from near-shore trapping, are thereafter spread offshore in coastal waters.

Using aerial photography and in situ measurements to estimate the quantity of macro-litter on beaches.

This study has demonstrated a reliable method of quantifying the total mass of litter on a beach. It was conducted on Ookushi beach, Goto-Islands, Japan, and uses a combination of balloon-assisted aerial photography and in situ mass measurements. The total mass of litter over the beach was calculated to be 716±259kg. This figure was derived by multiplying the litter-covered area (calculated using balloon-assisted aerial photography) by the mass of litter per unit area. Light plastics such as polyethylene made up 55% of all plastic litter on the beach, although more work is needed to determine whether lighter plastics are transported to beaches more readily by winds and ocean currents compared with heavier plastics, or whether lighter plastics comprise a greater percentage of marine litter. Finally, the above estimates were used to calculate the total mass of metals released into coastal ecosystems via plastic litter on beaches.

Identification of the biological species of Armillaria associated with Wynnea and Entoloma abortivum using PCR-rFLP analysis of the intergenic region (IGR) of ribosomal DNA.

Polymerase chain reaction restriction fragment length polymorphism (PCR-RFLP) analysis of the first intergenic region (IGR1) of nuclear ribosomal DNA was used to clarify the relationship between IGR1 variations and six Japanese biological species of Armillaria: A. gallica, A. nabsnona, A. ostoyae, A. cepistipes, A. mellea and Nagasawa's E (Nag. E: taxonomically unknown species). The procedure was then used to identify Armillaria species associated with Wynnea species (W. americana and W. gigantea) and Entoloma abortivum. By combining the RFLP patterns obtained using three endonucleases, HaeIII, HinfI and MspI, the IGR1s from 18 isolates of six Armillaria species were assigned to nine different RFLP phenotypes and the six species were distinguished from each other. Each of the RFLP phenotypes from the Armillaria isolates associated with Wynnea species or E. abortivum matched a corresponding phenotypes observed among the six Armillaria species. Based on this, all four isolates from W. gigantea were identified as A. mellea, two from W. americana as A. cepistipes, and all three from E. abortivum as Nag. E. These results provide new information on the biological species of Armillaria associated with Wynnea and E. abortivum.