Abstract:Minamata Bay which suffered from a major disaster called "Minamata Disease" has already remediated from 1977 to 1990 by carried out highly mercury (Hg) contaminated sediment and reclaimed it in the bay area. Furthermore, many studies reported that the mercury has reached Yatsushiro Sea, the outer part of Minamata Bay. It can be assumed that the sediment transport still occurs from remaining Hg concentration even after the remediation project. In order to investigate it, we try to simulate the transport of sedi… Show more
“…The effects of coastal topographical changes on benthic community assembly through changes in hydrodynamic and physicochemical regimes have been shown in both the Oiartzun estuary (Borja et al, 2013) and Pearl River estuary (Yang et al, 2018). However, a simulation study in Minamata Bay showed that reclamation slowed bottom current velocity from 6 to 3 cm/s at ebb tide (Fathya et al, 2016), which could help facilitate retention of larvae input from other areas. Marine biological communities are sometimes maintained by self‐retention of larvae from the site rather than by dispersal from other regions (Cowen & Sponaugle, 2009; Giangrande et al, 2017).…”
Approximately 30 years after mercury pollution remediation finished in Minamata Bay, we report here the present state of the subtidal benthic communities in Minamata Bay. The benthos was sampled at stations in Minamata Bay five times between July 2018 and 2019, capturing seasonal variations. Sediment characteristics were relatively stable across seasons. Sediments contained >80% silt-clay and had total organic carbon (TOC), total nitrogen (TN), and residual total Hg content (THg) approximately 20 mg/g, 2.0 mg/g, and 2.5 mg/kg (dry-weight basis), respectively, with a C/N ratio of $11. THg was positively correlated with TOC, whereas TOC was negatively correlated with the C/N ratio, suggesting that TOC is a proxy for sediment microalgal matter (i.e., settling phytoplankton and/or microphytobenthos), a potential food for macrobenthos. Macrobenthos abundance was very low (approximately 100 individuals/m 2 ) and the maximum effective number of species was three in all seasons. We detected effects of THg on species richness and composition of the community, but not on total macrobenthos abundance, biomass, species diversity, or relative species abundance. The TOC gradient was significantly related to both species composition and relative abundance of the community.However, the total variation explained by both TOC and THg for community composition was low (10% at most). These results suggests that other environmental factors, such as the alteration of hydrodynamic and physicochemical regimes caused by the reclamation for pollution mitigation, may also have had a long-lasting effect on community assembly and the present poor macrofauna levels in Minamata Bay.
“…The effects of coastal topographical changes on benthic community assembly through changes in hydrodynamic and physicochemical regimes have been shown in both the Oiartzun estuary (Borja et al, 2013) and Pearl River estuary (Yang et al, 2018). However, a simulation study in Minamata Bay showed that reclamation slowed bottom current velocity from 6 to 3 cm/s at ebb tide (Fathya et al, 2016), which could help facilitate retention of larvae input from other areas. Marine biological communities are sometimes maintained by self‐retention of larvae from the site rather than by dispersal from other regions (Cowen & Sponaugle, 2009; Giangrande et al, 2017).…”
Approximately 30 years after mercury pollution remediation finished in Minamata Bay, we report here the present state of the subtidal benthic communities in Minamata Bay. The benthos was sampled at stations in Minamata Bay five times between July 2018 and 2019, capturing seasonal variations. Sediment characteristics were relatively stable across seasons. Sediments contained >80% silt-clay and had total organic carbon (TOC), total nitrogen (TN), and residual total Hg content (THg) approximately 20 mg/g, 2.0 mg/g, and 2.5 mg/kg (dry-weight basis), respectively, with a C/N ratio of $11. THg was positively correlated with TOC, whereas TOC was negatively correlated with the C/N ratio, suggesting that TOC is a proxy for sediment microalgal matter (i.e., settling phytoplankton and/or microphytobenthos), a potential food for macrobenthos. Macrobenthos abundance was very low (approximately 100 individuals/m 2 ) and the maximum effective number of species was three in all seasons. We detected effects of THg on species richness and composition of the community, but not on total macrobenthos abundance, biomass, species diversity, or relative species abundance. The TOC gradient was significantly related to both species composition and relative abundance of the community.However, the total variation explained by both TOC and THg for community composition was low (10% at most). These results suggests that other environmental factors, such as the alteration of hydrodynamic and physicochemical regimes caused by the reclamation for pollution mitigation, may also have had a long-lasting effect on community assembly and the present poor macrofauna levels in Minamata Bay.
“…3). In the horizontal direction, the variable grid established by Fathya et al 14) was utilized, where the grid accuracy of Minamata Bay, and its surrounding regions is up to 62.5 m, whereas the grid accuracy of places further from Minamata Bay is 125 m and 250 m, respectively. The vertical grid adopts the σ coordinate system and is composed of five layers, each having 20% of the total depth.…”
Section: Methodology (1) Sample Collection and Processingmentioning
In 1977, the Minamata Bay Pollution Prevention Project was initiated to dispose of sedimentary sludge containing over 25 ppm of total mercury (T-Hg) after the outbreak of Minamata Disease. The sediments containing the high concentration Hg were dredged, but nevertheless, the residual Hg in Minamata Bay has attracted much attention. Moreover, some studies have even indicated that the Hg remaining in the sediments near the bay has migrated to the Yatsushiro Sea.In this study, the vertical distribution of mercury concentration across sediment layers at different sites was investigated. Developed numerical modeling was used to evaluate the impact of sediment particle size on the migration of Hg-containing sediments from Minamata Bay to the Yatsushiro Sea as well. According to the results, mercury migrated from Minamata Bay to the Yatsushiro Sea, where the mercury migrating to the southwest of the Yatsushiro Sea is more concentrated. Additionally, there were significant differences in mercury concentrations at various depths and locations. The total mercury content varied with the particle size. The migration of mercury-containing sediments with larger particle size was slower and the migration range was limited.
“…The calculation domain in the model was defined to contain both the Yatsushiro Sea and the Ariake Sea. The horizontal grid is a variable grid established by Fathya et al 14) , and the grid precision is 62.5 m, 125 m, and 250 m, respectively. The vertical grid adopts the σ coordinate system and consists of five layers, each of which is 20% of the total depth.…”
Section: ) Establishment Of Numerical Modelmentioning
After Minamata disease occurred in Kumamoto Prefecture, the Minamata Bay Pollution Prevention Project on Minamata Bay area was started to deal with mercury pollution. Beneficial from the project, the mercury content in the bay area has been significantly reduced. However, many studies have shown that the residual trace mercury content around the bay is still high. Furthermore, mercury has migrated from Minamata Bay to the Yatsushiro Sea. Therefore, continuous research on the distribution and content of mercury in this region is required.In this study, using sediment classification, the relationship between sediment particle size, particle specific surface area, and T-Hg (total mercury) concentration was investigated. Based on the numerical simulation, the particle size effect on the migration of mercury-containing sediments and the T-Hg distribution in the Yatsushiro Sea were studied. The result showed that the larger the particle size, the lower the T-Hg concentration in the sediment. Meanwhile, the larger the particle specific surface area, the higher the T-Hg concentration. Moreover, the smaller the particle size of the mercury-containing sediment, the higher the migration speed as well as the more comprehensive migration range. From the numerical simulation results, it was found that mercury was mainly distributed in the southwest and northeast directions from Minamata Bay. Finally, the simulated mercury distribution, which considers the relationship between particle size and mercury concentration, shows a high agreement with the past measurements of mercury, suggesting the importance of particle size effect in mercury migration.
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