Abstract
An explosive volcanic eruption occurred in the Ogasawara Islands on 13–15 August 2021, bringing unprecedented amounts of floating pumice to the coast of Okinawa Island in the Ryukyu Archipelago, 1300 km west of the volcano, approximately 2 months later. The coast of Okinawa Island, especially along the northern part, is home to many typical subtropical seascapes, including coral reefs and mangrove forests, so the possible impact of the large amount of pumice is attracting attention. Here, we report early evidence of ecosystem changes as a result of large-scale pumice stranding on coastal beaches, in estuaries and mangrove forests and passage across fringing coral reefs. Massive pumice drifts are major obstacles to fishing activities and ship traffic, but short and long-term changes in coastal ecosystems can also occur. The phenomena observed on Okinawa Island can be a preview of coastal impacts for the Kyushu, Shikoku, Honshu Islands, where pumice has subsequently washed ashore.
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Introduction
Pumice rafts can recruit and transport a huge biomass and a wider variety of marine organisms greatly facilitating marine species dispersal1,2,3,4,5,6, but large amounts of floating pumice have the potential to become a natural disaster as a result of human impact7. In this paper, we report on the first arrivals of a pumice raft that drifted towards the main island of Okinawa, located in the Southwest Islands of Japan. Okinawa Island is located in the southern region of Japan and has a high level of biodiversity along its coast, including coral reefs, mangroves, and tidal flats8,9,10. Okinawa is influenced by the warm Kuroshio Current (Fig. 1), which flows northward along the west side of the island11,12, making the marine environment suitable for tropical and subtropical organisms8,9,13. The island therefore has high touristic value, but some areas are threatened by rapidly increasing tourism pressure14,15,16 from ongoing coastal developments8,13,17, in parallel with the global changes resulting from multiple human activities18,19,20. In contrast, little coastal development has occurred in the northern part of Okinawa Island, the site of Yambaru National Park, with a high level of biodiversity in the coastal marine environment. In 2021, the region, together with the Yambaru region and Amami Oshima, Tokunoshima, and Iriomote Islands, was named a World Natural Heritage Site21.
The Japan Coast Guard reported that a large submarine eruption occurred within the Ogasawara Archipelago (Fukutoku-Oka-no-Ba, Tokyo, Japan: 24.285°N, 141.481°E) on 13 August 202122. Eruption details have been summarized by the Geological Survey of Japan, National Institute of Advanced Industrial Science and Technology23, Smithsonian Institution Global Volcanism Network24, and Yoshida et al.25. Satellite observations were able to capture the formation and then dispersal of the 300-km2 pumice raft26. Pumice is a highly vesiculated glassy volcanic rock fragment where the vesicularity typically ranges from 50–80% making the pumice have a bulk density less than water. It is commonly light colored, reflecting a high silica content25. The large amount of pumice stones produced by this eruption was carried by surface winds and ocean currents for approximately 2 months before reaching the Ryukyu Islands, including the main island of Okinawa, which is located approximately 1300 km away from the volcano (Fig. 1).
In this initial report, we describe the effects of a massive pumice drift on natural systems in the coastal area of northern Okinawa Island (Fig. 1b; Supplementary Table 1) and infer how the ongoing presence of pumice rafts may impact the coastal ecosystem via biological responses to this novel habitat formation. Because of the ever-changing spread of the pumice raft, observations were made at the time and soon after first arrival along the coast of the Yambaru region (Kunigami Village), which is particularly rich ecosystem21.
Results and discussion
Massive drift of pumice along the northeastern coast of Okinawa Island
A large amount of pumice stones reached and was deposited along the northeastern coast of Okinawa Island, that were brought by strong seasonal northeasterly winds (Supplementary Video 1). The pumice was thought to be brought by the Kuroshio countercurrent from sites near the Ogasawara Archipelago 1300 km away. Because the Kuroshio countercurrent is composed of various medium-sized eddies in the ocean, the current does not always flow in one direction and as a continuous flow27,28. The pumice drift was more strongly controlled by the seasonal northwesterly winds to be transported to Okinawa across the Philippine Sea (Fig. 1a). The pumice raft reached the northern part of Okinawa approximately 2 months after the eruption (Figs. 2, 3 and 4). According to a very recent report, the pumice clasts were drifting ashore in Thailand (traveling 4000 km-long distance) across the South China Sea within half a year of this eruption29. Most pumice stones were gray, but some pumice was banded, and others were black reflecting some compositional variation25,29 (Fig. 2d,e). The Kuroshio Current is faster than the Kuroshio countercurrent27, so some pumice clasts have already reached the main island of Japan25. Tracking the dispersal of the pumice will allow a better forecasting model based on observed raft trajectories by considering exact wind effects in the Philippine Sea30.
Changes in the coastal landscape: natural beaches and estuaries
Marine calcifiers, including corals, calcareous algae, and foraminifers, produce white sandy beaches on Okinawa Island. However, the gray pumice drifting ashore changed the white sand beach, especially along the northeastern coastline. We observed several lines of pumice aggregations, suggesting that pumice was brought ashore by wavefronts several times produced by a strong north wind at the tide lines (Supplementary Video 1; Fig. 2a). At the same sampling site, the thickest depth of beached pumice was more than 30 cm (Fig. 2b; Supplementary Video 2). Most of the pumice stones were from 0.5 cm to 3 cm in diameter, with a few black pumice stones included (Fig. 2c: yellow arrow). Pumice stones arrived at the estuaries of some brackish rivers (Fig. 8, Supplementary Fig. 1a) and mangrove forests in northwest Okinawa (Fig. 9).
Pumice stones and pumice rafts show dynamic behavior in a short period. We captured photographs 24 h apart at two positions on the shore of Okinawa, which allowed us to compare the pumice dynamics during this period (Fig. 3). Within that time frame, there were two high tides, and the tide level changed by up to 170 cm. As seen in Fig. 3a, on the first day, the coast was covered with pumice, and floating pumice could be seen on the seafront. The north wind was strong that day, as shown by the relatively high waves near the shore as well as white‐crested waves near the reef edge. By the following day, most of the pumice had been moved offshore by tides and winds (Fig. 3b), indicating that newly beached pumice raft deposits were removed quickly from open beach areas. At another site on a gravelly beach, pumice fully covered the seawall on the first day, but almost all of the pumice stones were washed away, leaving the original gravels, on the following day (Fig. 3c,d). Japan Meteorological Agency (Oku station: 232 m above sea level, latitude 26°50.1, longitude 128°16.3') reported that northerly winds were blowing (mean wind speed: 3.4 m/s) on 23rd October in northern Okinawa. The following day, the wind direction changed to the east-southeast; blowing offshore (mean wind speed: 2.9 m/s), resulting in the dramatic removal of pumice form the coast (Fig. 3). These observations indicate that surface winds rather than ocean currents had a strong influence on the raft trajectory and residence time on beaches, and are consistent with past research5. These observations lead us to expect that the pumice rafts will disappear from the coast of Okinawa fairly quickly, but in fact, there have been many cases where they have come back again in a few days. Although the overall amount of pumice drifting has been decreasing, a small amount of pumice has been drifting in coastal area of Okinawa in May, 202231. It is unlikely that large amounts of pumice will drift repeatedly throughout Okinawa Prefecture as reported in this report, but it should be noted that detached pumice material remains in beach and river runoff.
Biofouling of sessile organisms on pumice arriving to Okinawa
It is noteworthy that the pumice rafts traveled over the deep Philippine Sea for over 2 months, and on arrival in Okinawa there was little to no biofouling of the pumice (Fig. 2). Some stranded pumices observed on Okinawa beaches had become habitats for sessile organisms (Fig. 4), as reported in previous studies1,2,3,4,5,6,29. Goose barnacles (Lepas sp.) without external damage to the shell were the most abundant species observed on the pumice (Fig. 4b). Lepas is a common biofouling taxon distributed globally and plays a role in biofouling as a foundation organism. The shell growth rate is more than 1 mm/day in some Lepas species32 suggesting that the Lepas had been growing on the pumice for about two weeks. Measurements of the shell size of Lepas attached to the pumice collections conducted in the same area (Supplementary Video 2) showed a bias toward larger sizes in the second collection (5.92 ± 3.86 mm (average ± S.D.), n = 75, 13 November 2021) than in the first one (3.43 ± 1.08 mm, n = 21, 31 October 2021), and significant differences were detected between the measurement periods (Mann–Whitney U test, p < 0.05). These data imply that the barnacles settled on the pumice stones and started to grow near Okinawa. The shell size would be larger if the barnacles had settled and grown on the surface of the pumice near the Ogasawara Islands as because the travel time was at least 50 days to Okinawa. The pumice raft crossed deep ocean water of the Philippine Sea from the source volcano and had no island or reef encounters on the way; it therefore could not recruit shallow marine organisms like Lepas early. This is a big difference to the pumice rafts in the Southwest Pacific1,5,6. A cheilostome bryozoan was also found on the same pumice sample (Fig. 4c). Bryozoans are colonial marine invertebrates that construct an exoskeleton composed of aragonite and calcite33,34.
Red autofluorescence was detected from the pumice surface (Fig. 4d), thought to be derived from the chlorophyll of microalgae. After treating with acetone and methanol, autofluorescence from pumice dramatically disappeared (see Supplementary Fig. 2) with a diameter of several tens of micrometers (Fig. 4e, f). The texture of the pumice clasts (Fig. 4d) and the bright spots of the red fluorescent signal (Fig. 4e) were not completely coincidental. Red signals are more prominent in the vesicle depressions rather than on the outer surfaces where abrasion would occur. As the pumice pebbles in the rafts are constantly rubbed and worn, only microorganisms are likely to survive on the surface on small pumice pebbles. Once deposited in estuaries and in brackish water, filamentous algae quickly grew on the pumice (Supplementary Fig. 3). Our study did not carry out species identification of microorganisms on pumice stones. However, Naya & Hatanaka35 already discussed a possibility that pumice rafts may contribute to the dispersal of some attached marine diatoms.
Genetic studies have revealed the transport of larval corals36 and crown-of-thorn starfish37 between the Okinawa and Ogasawara Archipelagos, which are more than 1000 km apart, with no large islands in between. Given that corals can be transported long-distances on pumice1,2,3,5,6, integrating spatiotemporal information on the exact pumice movement on the sea surface with such genetic analyses may help to clarify the dispersal processes of marine organisms in greater detail.
Considering that small sessile organisms were often found on pumice rafts (Fig. 4), it is easy to imagine that pumice rafts transport not only multicellular organisms but also microorganisms such as bacteria. Some astrobiology studies have proposed that pumice might have functioned as a habitat for the earliest settlements of microorganisms38,39. Considering this study, pumice rafts may serve a variety of functions in bacterial ecosystems, such as connecting populations over long distances1,2,3,4,5,6 and serving as a direct link between sandy beaches and the ocean (Fig. 3). Pumice has a large surface area with many vesicles40,41,42. When pumice stones are impacted onto solid surfaces such as by wave action, they may break apart, thus enlarging the surface area and leading to a dramatic increase in available bacterial habitat; pumice may continue to serve as an ecosystem mediator for a long period of time.
Impacts on fishes and other organisms in coastal waters
One portion of the pumice raft reached the Hentona fishing port (Fig. 5a), where more than 200 farmed Indian mackerel (Rastrelliger kanagurta) had died in the fishery cages in the bay by early November (Fig. 5b). Fish stomachs were filled with pumice stones (Fig. 5c), suggesting that they had confused pumice for food. The digestive system in the fish is filled with numerous pumice stones, and in places, the pumice stones are visible through the intestinal wall or are damaged, suggesting that the direct cause of death of the farmed fishes was not starvation but damage to the fish's digestive tissues. This species of fish is a filter feeder swimming with its mouth open while feeding. The same feeding behaviour is also seen in the fin whale (Balaenoptera physalus) and basking shark (Cetorhinus maximus), two marine species studied with regard to environmental pollution by microplastic debris43. When marine wildlife such as turtles, seabirds, and whales mistake floating plastic waste for prey, most die of starvation, as their stomachs become filled with plastic debris44,45. We are concerned that a similar situation may occur with filter-feeding fishes mistakenly consuming pumice stones.
Some migratory fishes must swim with their mouths open and breathe by constantly taking oxygen dissolved in the seawater passing through their gills (e.g., tuna, bonito, yellowtail, sardine, mackerel, swordfish and basking shark). If pumice pebbles or particles were to pass through the gills, depending on clast size, they may physically damage the tissue. This damage may affect the survival of these economically important fishes and perhaps alter their population dynamics. Thus far, it is unclear how the catches in the seas around Okinawa have changed since the arrival of the drifting pumice. If this hypothesis is correct, then pumice traveling on the Kuroshio Current could also affect fisheries in the seas around Japan. Through more research, the impact of large quantities of pumice on marine life will become clearer in the future.
Pumice rafts may also affect the upriver migration of fishes46,47, which move between the sea and rivers according to their life histories. Pumice covered the brackish estuary of the Oku River in northwest Okinawa (Oku River, Supplementary Fig. 1a), adjacent to the Oku harbor (Supplementary Fig. 1b). We observed that pumice stones covered the river bottom as well as mangrove mudflats. Further studies are needed to assess the impacts of pumice rafts on anadromous and amphidromous fish populations.
Coral reef interactions
Coral reefs are diverse ecosystems and provide coastal protection from waves48. Reef-building corals maintain photosynthetic algae (zooxanthellae) that live in their tissues and play a critical role in supplying the coral with glucose, glycerol, and amino acids, which are the products of photosynthesis under energetic consequences of flexible symbiont associations (i.e., mutualistic relationships)49. If the symbiotic relationship breaks down, the coral tissue will turn white (bleaching), and in the worst case, the coral will die50,51. Besides, pumice rafts may provide the opportunity for any attached species to escape from local unfavorable conditions. Previous studies have shown that pumice rafts contribute to coral dispersal1,2,3,5,6. But potential long-term impacts of pumice rafts on coral reefs remain unknown. At Okinawa, pumice rafts washed ashore in inland bays such as beaches (Figs. 2, 3) and concentrated in harbors (Fig. 5, Supplementary Fig. 1b,c), but such areas are not often inhabited by corals. Where pumice rafts were observed to pass over fringing coral reefs, sunlight was temporarily reduced (Fig. 6b). No sustained coverage of the fringing reefs was observed to indicate any photosynthesis was inhibited, causing negative effects for coral physiology.
Locally, small pumice pieces occasionally hit shallow corals in response to breaking waves across the fringing reef (Fig. 7, Supplementary Video 4). In larger pumice rafts and containing larger pieces of pumice, a potential exists for surface damage and stress to corals by pumice impacts. Reef-building corals have a fragile layer of soft tissue on a calcium carbonate skeleton. To protect and defend themselves from various kinds of foreign matter in the environment (e.g., sand and bacteria), coral tissues continuously produce mucus, which is thought to play a role in coral halobiont defense, possibly through the production of antimicrobial substances52. Microscopic scratches may be caused by drifting pumice stones, which could induce inner tissue exposure and the loss of mucus function. This situation may lead to infection of the coral surface by bacteria and other pathogens if adhered to the pumice stones. Previous studies have reported that coral tissue can be lost in response to mechanical stress leading to the induction of coral diseases16, and multiple environmental stressors could result in the expansion of harmful bacteria in the reef environment53,54. Currently, the exact impact of the pumice on the coral reef ecosystems around Okinawa is unclear, but the systems should be closely monitored.
Impact on mangrove ecosystems caused by sudden changes in sediment properties
In the tropics and subtropics, mangrove ecosystems play critical roles in interactions between land and sea. In fact, mangrove ecosystems are linked to neighboring environments such as coral reefs and seagrass beds through the movement of organisms and the circulation of materials55,56. Recent scientific advances have clarified the microbial environment of mangroves by using microarray-based genomic technology for detecting functional genes. Their unique microbiota suggests that they may perform several important functions, such as recycling nutrients, destroying pollutants, and treating anthropogenic wastes. Many antibiotic and metal resistance functional genes are detected57.
More protracted deposition of pumice stones occurred in estuaries around Okinawa characterized by mangroves (Fig. 8). A river flowing through a mangrove forest connects to Ibu Beach (Fig. 2a: white arrow points to the river mouth). In the brackish water of the river, approximately 100 m from the mouth, many pumice stones were found to have sunk (Fig. 8, 9a). The pumice stones were easily moved by hand, suggesting that the pumice had not completely lost its buoyancy, and some of the pumice stones at the bottom of the river swayed slowly in the water flow (Supplementary Video 5). For a goby (Psammogobius biocellatus) on the river bottom seemed to have already acclimatized to the environment, at the boundary between the pumice stones and conventional sediment (Fig. 8c). Further up the river (approximately 200 m from the river mouth), floating pumice stones reached the point where orange mangrove (Bruguiera gymnorhiza) trees were growing (Fig. 8d). There was no heavy rainfall during the field observation period. If heavy rains occur and the flow rate of the river increases, however, pumice stones could be cleaned out of the estuaries and be transported back to the ocean. It will be necessary to monitor river substrate changes and to assess how pumice might affect river and estuary ecosystems (e.g., fish migration) in the future46,47. Within four months of the massive pumice adrift to Okinawa Island, we could easily observe green filamentous algae sprout from pumice pebbles (Supplementary Fig. 3). Our observations are consistent with those already reported in previous studies2,4,5,6.
Pumice rafts also drifted onto the mangrove mudflats (Fig. 9a), which were almost completely covered with pumice pebbles (Fig. 9b). Although this area is covered with a massive amount of pumice, many of the crabs and gobies survived under these circumstances (Fig. 9c–i), and we did not find any evidence of mass die-offs in the pumice-covered mangrove at the beginning of this study period. However, the surface layer of the crab burrow was covered with pumice and was prone to collapse; in some cases, the crab burrows were blocked (Fig. 9g). Observations of behavior, with particular focus on a fiddler crab (Uca lactea lacteal) in Fig. 9c, showed that in some cases, it had given up trying to enter the burrow, which easily collapsed under the pumice stones (Supplementary Video 6). In another case, competition to acquire burrows emerged, making it difficult for smaller individuals to obtain a burrow even within the same species (Supplementary Video 7). The pumice-covered substratum is different from the original mud substratum, making it a particularly difficult environment for small crabs. To adapt to this environment, small crabs have already shown alternative behaviors, such as hiding in the spaces among pumice pebbles (Fig. 9h). Fiddler crabs use their claws to put substrates in their mouth and then sift through the substrate and eat the organic matter (e.g., algae, fungi, and tiny insects)58. As the substrate has been replaced by pumice instead of sand, feeding behavior may be inhibited, especially for smaller individuals. If pumice stones occupy a large surface area during the breeding season, however, they may interfere with the spawning and larval dispersal of these crabs. Three months after we started the survey, we could hardly observe the burrows of the fiddler crab or their population on the pumice cover mudflat. It is speculated that the environment where the fiddler crabs live was covered with pumice pebbles, hindering eating behavior, with the younger individuals being more affected.
Another observed mangrove inhabitant is the mudskipper (Periophthalmus argentilineatus), a fish that jumps on the surface of the water around a creek near the riverbank. However, when the pumice grains stuck to the fish’s body, they did not move well and appeared to sink (Supplementary Video 8). The mudskipper has relatively thin skin that is suitable for life on land and breathing oxygen59, such that fish movement may result in the pumice on its skin surface causing microinjuries. A recent molecular study suggested that the expansion of innate immune system genes in mudskippers may provide a defense against terrestrial pathogens60. Because the bacterial composition of the sediment may also be changed by drifting pumice stones, the immune response of this fish may be altered if the pumice pebbles remain on the mudflats for a long time. We are also concerned about mudskippers’ feeding activities as well as territorial and courtship behavior on pumice-covered mangroves61. In addition, the mudskipper has a special egg-laying behavior: the fish deposits eggs on the walls of an air-filled chamber within its burrow to provide air to the eggs in the lower oxygen conditions in the mud62. Likewise, the various behavioral patterns of gobies could also be affected by the drift of pumice in the mangrove. In addition to mangrove fishes, we assume that drifting pumice stones may especially affect fish communities inhabiting soft-sediment coastal areas where pumice pebbles easily sink or bury the soft sediment10.
As described above, the organisms living in the mangrove tidal flat have difficulty finding shelter due to the change in the substrate (Fig. 9c–i, Supplementary Videos 6–8). Thus, it is likely to be preyed upon by other wild animals, such as the Okinawa rail (Hypotaenidia okinawae). H. okinawae is a flightless rail that is declared the National Natural Treasure (Agency for Cultural Affairs) and endemic to Yambaru region (Supplementary Videos 9). The pumice-covered mangrove flats should provide an efficient feeding ground for the Okinawa rail or other birds for a while. On the island of Okinawa, pumice covered a wide area of the coast, which may alter the behavior patterns of various organisms associated with the area. Although the Okinawa rail is not a seabird a recent study reported that migratory birds ingest pumice stones when they were starving45. Changes in the behaviors of migratory birds in areas where pumice rafts occupy fishing areas or have been washed ashore may require more attention.
Impact on local industries and countermeasures of massive pumice stone arrival
The local broadcast stations in Okinawa Prefecture reported that a large amount of pumice aggregated in some fishing harbors in northern Okinawa, advising that pumice stones can damage the propellers of fishing boats and cause engines to overheat. Fishing boats were unable to operate because their drive systems malfunctioned; for example, as the engine coolant system became clogged with pumice, the engine overheated. According to interviews conducted by the Okinawa Prefectural Fisheries Division with local fishing cooperatives, massive pumice stone drifts caused engine trouble in 206 fishing boats (about 7%). In addition, 45 fishing boats were temporarily disabled (about 1.5%) in Okinawa Prefecture in the period up until May 13, 202231. Thus, not only fishing but also the tourism industry is likely to be affected if this situation continues for a very long period. The massive amount of pumice entering enclosed harbours preventing the ready exchange of seawater makes it difficult for the pumice stones to be removed via natural means (Fig. 5, Supplementary Fig. 1b,c), so in some cases removal work was done by heavy machinery. Oil fences were installed to prevent pumice from entering some harbors.
To minimize the impact of pumice rafts on coastal infrastructure such as ports and harbours, it will be necessary to make advances in predicting the movement of pumice rafts as well as to develop countermeasures for future events. Volcanic activity is common in Sakurajima (Kagoshima Prefecture. Because of this situation, the local port has performed a workload analysis of how to remove drifting pumice after the likely event of a major volcanic eruption63. Likewise, assessing the effects of pumice rafts will provide valuable information for planning disaster prevention in Okinawa and other areas in the future.
Here, we describe the possibility of pumice stones serving as a nutrient adsorbent material. Nitrate and phosphate from local and industrial wastewater are the main sources of nutrient loading in the marine environment64,65, and these compounds induce the reduction of dissolved oxygen in the ocean66. Pumice-associated nutrient uptake driven by microbial activity was suggested, after the pumice rafts created on lake Nahuel Huapi and Lake Espejo following the Puyehue-Cordón Caulle (Chile) eruption in June 201139. The possible role of pumice stones in marine biogeochemical cycles is a topic for future research.
Conclusions
We reported some examples of the early influences of arriving pumice rafts on a broad range of coastal organisms found on coastal beaches, in estuaries, coral reefs, and mangrove forests. In addition to the impact on fishing activities and ship traffic as a navigational hazard, possible future long-term changes in coastal ecosystems may result from the pumice stranding and persistence in coastal environments. Drifting pumice stones are not only useful for dispersing marine organisms but may have other functions, such as a medium for dispersing the microbiome and the possibility of absorbing nutrients from seawater. Pumice has been carried by the Kuroshio Current and has since affected the coastal environments of Kyushu, Shikoku, and Honshu Islands of Japan. Pumice rafts have also recently reached Taiwan, Philippines, and Thailand which are even further away from the source volcano. We hope this report of the situation will be helpful for additional research carried out in Okinawa and other places where pumice stones have been washed ashore, as further investigations are needed to clarify how the large amount of pumice affects both marine and shallow-water environments. Although the peak of pumice drift seems to have passed within the observation period, long-term investigation is necessary.
Methods
Okinawa Island does not belong to dry climate zone and thus the surround coasts are not classified as arid nor semi-arid coasts67 There are no large rivers nearby and the area is not fed by river sediments. The sedimentary coasts bordering Okinawa Island are mainly formed by marine-biogenic material including corals and foraminifera, together with limited contribution of eolian dust68,69. Since the pumice rafts were found at Cape Hedo on 16 October 2021, we commenced a survey focusing on the Yambaru region every weekend. Underwater photography at the reef edge was conducted on 14 November 2021. Drone photography (Fig. 5a) was conducted by Okinawa Times Co., Ltd., which is a local media outlet in Okinawa Prefecture. The images in Figs. 5b and c were provided by the Kunigami Fishing Association. A Coolpix w 300 (Nikon Co., Ltd.) was used to take the photographs. The latitude and longitude of the locations where the images were taken are listed in Supplementary Table 1. The shell length measurement of Lepas sp. was carried out on pumice that had just washed ashore on the beach. The first samples were taken from seven pumice stones (31 October 2021), and the second collection were from six pumice stones (13 November 2021). Sampling was conducted by walking 200 m of the shoreline boundary looking for wet pumice with Lepas attached. Statistical analysis of shell size of them were analyzed with R version 4.0.3 software. Pumice pebbles were collected from a pumice raft at Ibu beach on 15 January 2022. A Leica M165 stereo microscope was used for pumice pebble observation. Pebbles were excited 485/10 nm with ET GFP/CY3 band pass filter. The red autofluorescent signal from algae was detected by a color digital camera (also see Supplemental Fig. 2, 3). The green autofluorescence from pumice, which may have come from the mineral, is minimal or absent under fluorescent microscopy. Adobe premiere pro and image J software were used for video and image editing.
Data availability
All data generated or analyzed during this study are included in this published article and its supplementary information files.
References
Jokiel, P. L. Transport of reef corals into the Great Barrier Reef. Nature 347, 665–667 (1990).
Jokiel, P. L. Rafting of reef corals and other organisms at Kwajalein Atoll. Mar. Biol. 101, 483–493 (1989).
Jokiel, P. L. & Cox, E. F. Drift pumice at Christmas Island and Hawaii: Evidence of oceanic dispersal patterns. Mar. Geol. 202, 121–133 (2003).
Velasquez, E. et al. Age and area predict patterns of species richness in pumice rafts contingent on oceanic climatic zone encountered. Ecol. Evol. 8, 5034–504610 (2018).
Bryan, S. E. et al. Pumice rafting and faunal dispersion during 2001–2002 in the Southwest Pacific: Record of a dacitic submarine explosive eruption from Tonga. Earth Planet. Sci. Lett. 227, 135–154 (2004).
Bryan, S. E. et al. Rapid, long-distance dispersal by pumice rafting. PLoS ONE 7, e40583 (2012).
Oppenheimer, C. Climatic, environmental and human consequences of the largest known historic eruption: Tambora volcano (Indonesia) 1815. Prog. Phys. Geogr. 27, 230–259 (2003).
Iguchi, A. & Hongo, C. (eds) Coral Reef Studies of Japan (Springer, New York, 2018).
Reimer, J. D. et al. Marine biodiversity research in the Ryukyu Islands, Japan: Current status and trends. Peer J. 7, e6532 (2019).
Kunishima, T. & Tachihara, K. Patterns in diversity and species composition in soft-sediment tidepool fishes across topographical types: Implications for conservation with spatial nuances. Mar. Environ. Res. 170, 105442 (2021).
Andres, M. et al. Study of the Kuroshio/Ryukyu current system based on satellite-altimeter and in situ measurements. J. Oceanogr. 64, 937–950 (2008).
Japan Coast Guard. Quick Bulletin of Ocean Conditions No. 207 (published on 5 November 2021) https://www1.kaiho.mlit.go.jp/KANKYO/KAIYO/qboc/2021cal/cu0/qboc2021207cu0.html
Veron, J. E. N. Conservation of biodiversity: A critical time for the hermatypic corals of Japan. Coral Reefs 11, 13–21 (1992).
Tada, O. Constructing Okinawa as Japan’s Hawaii: From honeymoon boom to resort paradise. Jpn. Stud. 35, 287–302 (2015).
Toyoshima, J. & Nadaoka, K. Importance of environmental briefing and buoyancy control on reducing negative impacts of SCUBA diving on coral reefs. Ocean Coast. Manage. 116, 20–26 (2015).
Lamb, J. B., True, J. D., Piromvaragorn, S. & Willis, B. L. Scuba diving damage and intensity of tourist activities increases coral disease prevalence. Biol. Conserv. 178, 88–96 (2014).
Reimer, J. D. et al. Effects of causeway construction on environment and biota of subtropical tidal flats in Okinawa, Japan. Mar. Pollut. Bull. 94, 153–167 (2015).
Hoegh-Guldberg, O. & Bruno, J. F. The impact of climate change on the world’s marine ecosystems. Science 328, 1523–1528 (2010).
Henson, S. et al. Rapid emergence of climate change in environmental drivers of marine ecosystems. Nat. Commun. 8, 14682 (2017).
Silvy, Y., Guilyardi, E., Sallée, J. B. & Durack, P. Human-induced changes to the global ocean water masses and their time of emergence. Nat. Clim. Chang. 10, 1030–1036 (2020).
United Nations Educational, Scientific and Cultural Organization (UNESCO): https://whc.unesco.org/en/list/1574/ (2021).
Hydrographic and Oceanographic Department Japan Coast Guard: Fukutoku-Oka-no-Ba submarine volcano information; https://www1.kaiho.mlit.go.jp/GIJUTSUKOKUSAI/kaiikiDB/kaiyo24-2.htm
Geological Survey of Japan: Fukutoku-Oka-no-Ba submarine volcano information; https://www.gsj.jp/en/hazards/volcano/fukutokuokanoba2021-e.html (2021).
Smithsonian Institution National Museum of National History Global Volcanism Program: https://volcano.si.edu/volcano.cfm?vn=284130
Yoshida, K. et al. Variety of the drift pumice clasts from the 2021 Fukutoku-Oka-no-Ba eruption, Japan. Isl. Arc. 31, e12441 (2022).
Maeno, F. et al. First timeseries record of a large-scale silicic shallow-sea phreatomagmatic eruption. Res. Square https://doi.org/10.21203/rs.3.rs-1272855/v1 (2022).
Kagimoto, T. & Yamagata, T. Seasonal transport variations of the Kuroshio: An OGCM simulation. J. Phys. Oceanogr. 27, 403–418 (1997).
Tada, N. et al. Drift of an ocean bottom electromagnetometer from the Bonin to Ryukyu Islands: Estimation of the path and travel time by numerical tracking experiments. Earth Planets Space 73, 1–12 (2021).
Yoshida, K. et al. Voyage to the west: Pumice raft from the Fukutoku-Oka-no-Ba in the northwest Pacific drifted over the South China Sea to Thailand. Earth ArXiv. https://doi.org/10.31223/X5PP9X (2022).
Application laboratory JAMSTEC (APL CHANNEL): https://www.youtube.com/playlist?list=PLKT1Tlr-tdGG85epmm6U9Gg7woBV4gd6p
Homepage for the Japanese municipality of Okinawa Prefecture: https://www.pref.okinawa.jp/site/kankyo/seibi/karuishihyoutyaku.html
Mesaglio, T. P. et al. The ecology of Lepas-based biofouling communities on moored and drifting objects, with applications for marine forensic science. Mar. Biol. 168, 1–16 (2021).
Taylor, P. D. & Sendino, C. Latitudinal distribution of bryozoan-rich sediments in the Ordovician. Bull. Geosci. 85, 565–572 (2010).
Knowles, T. et al. Interpreting seawater temperature range using oxygen isotopes and zooid size variation in Pentapora foliacea (Bryozoa). Mar. Biol. 157, 1171–1180 (2010).
Naya, T. & Hatanaka, Y. Preliminary report on diatoms attached to pumice clasts that originated from the 2021 eruption of the Fukutoku-Oka-no-Ba submarine volcano and drifted to Okinawa Island, southwestern Japan. Diatom 37, 84–88 (2021).
Nakajima, Y., Nishikawa, A., Iguchi, A. & Sakai, K. Regional genetic differentiation among northern high-latitude island populations of a broadcast-spawning coral. Coral Reefs 31, 1125–1133 (2012).
Horoiwa, M. et al. Integrated population genomic analysis and numerical simulation to estimate larval dispersal of Acanthaster cf. solaris between Ogasawara and other Japanese regions. Front. Mar. Sci. 8, 688139 (2022).
Brasier, M. D., Matthewman, R., McMahon, S. & Wacey, D. Pumice as a remarkable substrate for the origin of life. Astro. Biol. 11, 725–735 (2011).
Elser, J. J. et al. Community structure and biogeochemical impacts of microbial life on floating pumice. Appl. Environ. Microbiol. 81, 1542–1549 (2015).
Whitham, A. G. & Sparks, R. S. J. Pumice. Bull. Volcanol. 48, 209–223 (1986).
Fauria, K. E., Manga, M. & Wei, Z. Trapped bubbles keep pumice afloat and gas diffusion makes pumice sink. Earth. Planet. Sci. Lett. 460, 50–59 (2017).
Mitchell, S. J. et al. Sink or float: microtextural controls on the fate of pumice deposition during the 2012 submarine Havre eruption. Bull. Volcanol. 83, 1–20 (2021).
Fossi, M. C. et al. Large filter feeding marine organisms as indicators of microplastic in the pelagic environment: the case studies of the Mediterranean basking shark (Cetorhinus maximus) and fin whale (Balaenoptera physalus). Mar. Environ. Res. 100, 17–24 (2014).
Avio, C. G., Gorbi, S. & Regoli, F. Plastics and microplastics in the oceans: From emerging pollutants to emerged threat. Mar. Environ. Res. 128, 2–11 (2017).
Roman, L. et al. Desperate times call for desperate measures: Non-food ingestion by starving seabirds. Mar. Ecol. Prog. Ser. 662, 157–168 (2021).
Iida, M. et al. Specific gravity and migratory patterns of amphidromous gobioid fish from Okinawa Island, Japan. J. Exp. Mar. Biol. Ecol. 486, 160–169 (2017).
Milton, D. A. Living in two worlds: Diadromous fishes and factors affecting population connectivity between tropical rivers and coasts. In Ecological connectivity Among Tropical Coastal Ecosystems 325–355 (Springer, New York, 2009).
Harris, D. L. et al. Coral reef structural complexity provides important coastal protection from waves under rising sea levels. Sci. Adv. 4, eaao4350 (2018).
Davy, S. K., Allemand, D. & Weis, V. M. Cell biology of cnidarian-dinoflagellate symbiosis. Microbiol. Mol. Biol. Rev. 76, 229–261 (2012).
Baird, A. H., Bhagooli, R., Ralph, P. J. & Takahashi, S. Coral bleaching: The role of the host. Trends Ecol. Evol. 24, 16–20 (2009).
Dobson, K. L. et al. The effects of temperature, light, and feeding on the physiology of Pocillopora damicornis, Stylophora pistillata, and Turbinaria reniformis corals. Water 13, 2048 (2021).
Shnit-Orland, M. & Kushmaro, A. Coral mucus-associated bacteria: A possible first line of defense. FEMS Microbiol. Ecol. 67, 371–380 (2009).
Harvell, D. et al. Coral disease, environmental drivers, and the balance between coral and microbial associates. Oceanography 20, 172–195 (2007).
Kubomura, T., Yamashiro, H. & Reimer, J. D. Appearance of an anomalous black band disease at upper mesophotic depths after coral bleaching. Dis. Aquat. Org. 131, 245–250 (2018).
Alongi, D. M. Present state and future of the world’s mangrove forests. Environ. Conserv. 29, 331–349 (2002).
Meziane, T. & Tsuchiya, M. Fatty acids as tracers of organic matter in the sediment and food web of a mangrove/intertidal flat ecosystem, Okinawa, Japan. Mar. Ecol. Prog. Ser. 200, 49–57 (2000).
Bai, S. et al. GeoChip-based analysis of the functional gene diversity and metabolic potential of soil microbial communities of mangroves. Appl. Microbiol. Biotechnol. 97, 7035–7048 (2013).
Moruf, R. O. & Ojetayo, T. A. Biology of the West African fiddler crab, Uca tangeri (Eydoux, 1835)(Decapoda: Ocypodidae) from a mangrove wetland in Lagos, Nigeria. Int. J. Aquat. Biol. 5, 263–267 (2017).
Zhang, J., Taniguchi, T., Takita, T. & Ali, A. B. A study on the epidermal structure of Periophthalmodon and Periophthalmus mudskippers with reference to their terrestrial adaptation. Ichthyol. Res. 50, 310–317 (2003).
You, X. et al. Mudskipper genomes provide insights into the terrestrial adaptation of amphibious fishes. Nat. Commun. 5, 5594 (2014).
Clayton, D. & Townsend, K. Territoriality and courtship behavior. In Fishes Out of Water 277–300 (CRC Press, Florida, 2017).
Ishimatsu, A. et al. Mudskippers brood their eggs in air but submerge them for hatching. J. Exp. Biol. 210, 3946–3954 (2007).
Asano, T. & Nagayama, A. Analysis of workload required for removal of drifting pumice after a volcanic disaster as an aspect of a port business continuity plan: A case study of Kagoshima Port, Japan. Int. J. Disaster Risk Reduct. 64, 102511 (2021).
Borgesa, A. V. & Gypensb, N. Carbonate chemistry in the coastal zone responds more strongly to eutrophication than ocean acidification. Limnol. Oceanogr. Lett. 55, 346–353 (2010).
Carpenter, S. R. Phosphorus control is critical to mitigating eutrophication. Proc. Natl. Acad. Sci. U.S.A. 105, 11039–11040 (2008).
Rabalais, N. N. et al. Eutrophication-driven deoxygenation in the coastal ocean. Oceanography 27, 172–183 (2014).
Hzami, A. et al. Alarming coastal vulnerability of the deltaic and sandy beaches of North Africa. Sci. Rep. 11, 2320 (2021).
Inoue, K. & Naruse, T. Physical. Chemical, and mineralogical characteristics of modern Eolian Dust in Japan and rate of dust deposition. J. Plant Nutr. Soil Sci. 33, 327–345 (1987).
Naruse, T. Costal sand dunes in Japan. Geogr. Rev. Jpn. 62A–2, 129–144 (1989).
Acknowledgements
We greatly appreciate Kunigami Fishermen’s Association for providing us with photos and details of the eating behaviors of cultured Indian mackerel in the port while they were busy dealing with the removal of pumice stones. We also thank Okinawa Times Co., Ltd. for allowing us to use the aerial drone photo. This study was supported by the Research Laboratory on Environmentally Conscious Developments and Technologies (E-code) at the National Institute of Advanced Industrial Science and Technology. This research was also supported by a Grant-in-Aid for Research Fellow of Japan Society for the Promotion of Science Grant Number 21J01671.
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Y.O., A.I., and A.S. designed the field study. Y.O. conducted the fieldwork. A.I. performed statistical analysis. Y.O. made figures and videos. M.I., A.I., Y.O., and K.Y. conducted a microscopic observation. Y.O., A.I., M.I., K.Y., and A.S. wrote the paper. All authors gave final approval for publication and agreed to be held accountable for the work performed therein.
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Ohno, Y., Iguchi, A., Ijima, M. et al. Coastal ecological impacts from pumice rafts. Sci Rep 12, 11187 (2022). https://doi.org/10.1038/s41598-022-14614-y
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DOI: https://doi.org/10.1038/s41598-022-14614-y
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