Abstract:Since a large amount of MCs always suspends in the water in the reservoir and it has been discharged to the bay, suspension-feeding animals are exposed most seriously to the high levels of MCs occurring in these areas. We need to pay attention to the danger of widespread dispersal of MCs and biological concentration of MCs by fish and clam inside and outside the reservoir.
“…We counted the Microcystis cells in the water samples using a plankton counting chamber (MPC-200, Matsunami Glass, Osaka, Japan) under a microscope. For the determination of MCs, water and sediment samples were pretreated according to methods described by Umehara et al (2012). The concentration of MCs in the pretreated samples were measured by the immunoassay method using a Microcystin Plate Kit (Beacon Analytical Systems Inc., Portland, ME, USA) following the manufacturers recommendations.…”
Section: Methodsmentioning
confidence: 99%
“…Cyanobacteria, including a toxic species, Microcystis aeruginosa (Kütz. ), have bloomed repeatedly in the reservoir in the warm season since the mid-2000s, due to the extremely eutrophic conditions (Migita et al, 2006 Umehara et al, 2012). Water in the reservoir has often been discharged into the bay to maintain the water levels inside the reservoir.…”
Section: Introductionmentioning
confidence: 99%
“…According to data presented by the Ministry of Agriculture, Forestry and Fisheries, approximately 400 million m 3 of reservoir water is drained into the bay each year (Matsubase, 2008). Umehara et al (2012) reported the accumulation of MCs in the bottom sediment of Isahaya Bay due to the discharge of water containing MCs from the reservoir into the bay. However, the report only provided a causal connection between the reservoir and the bay, and the dynamics of MCs in the water of the bay are still unknown.…”
“…We counted the Microcystis cells in the water samples using a plankton counting chamber (MPC-200, Matsunami Glass, Osaka, Japan) under a microscope. For the determination of MCs, water and sediment samples were pretreated according to methods described by Umehara et al (2012). The concentration of MCs in the pretreated samples were measured by the immunoassay method using a Microcystin Plate Kit (Beacon Analytical Systems Inc., Portland, ME, USA) following the manufacturers recommendations.…”
Section: Methodsmentioning
confidence: 99%
“…Cyanobacteria, including a toxic species, Microcystis aeruginosa (Kütz. ), have bloomed repeatedly in the reservoir in the warm season since the mid-2000s, due to the extremely eutrophic conditions (Migita et al, 2006 Umehara et al, 2012). Water in the reservoir has often been discharged into the bay to maintain the water levels inside the reservoir.…”
Section: Introductionmentioning
confidence: 99%
“…According to data presented by the Ministry of Agriculture, Forestry and Fisheries, approximately 400 million m 3 of reservoir water is drained into the bay each year (Matsubase, 2008). Umehara et al (2012) reported the accumulation of MCs in the bottom sediment of Isahaya Bay due to the discharge of water containing MCs from the reservoir into the bay. However, the report only provided a causal connection between the reservoir and the bay, and the dynamics of MCs in the water of the bay are still unknown.…”
“…Recently, increases in lake eutrophication and cyanobacteria blooms have frequently occurred, seriously affecting water environmental safety (Sager 2009;Umehara et al 2012). Therefore, searching for a highly effective, safe, and simple cyanobacteria control method has become a study frontline and hot topic in the field of water environmental protection (Heisler et al 2008;O'Neil et al 2012).…”
Allelochemicals in Pistia stratiotes Linn. have a strong anti-cyanobacteria effect on Microcystis aeruginosa. To further determine the release routes of allelochemicals in P. stratiotes and understand their anti-cyanobacteria mechanisms, we aimed to systematically investigate the allelopathic effects of leaf leachates, leaf volatilization, root exudates, and residue decomposition of P. stratiotes on M. aeruginosa. The influences of P. stratiotes allelochemicals on the physiological properties of M. aeruginosa were also studied. Root exudates of P. stratiotes exhibited the strongest inhibitory effect on M. aeruginosa growth. The residue decomposition and leaf leachates exhibited a relatively strong inhibitory effect on M. aeruginosa growth. By contrast, the leaf volatilization stimulated M. aeruginosa growth. Therefore, root exudation was determined to be the main release route of allelochemicals from P. stratiotes. The mixed culture experiment of P. stratiotes root exudates and M. aeruginosa showed that the allelochemicals released from root exudation had no effect on the electron transfer of M. aeruginosa photosynthetic system II. However, it reduced the phycocyanin (PC) content and phycocyanin to allophycocyanin (PC/APC) ratio in the photosynthetic system. As the root exudates concentration increased, the electrical conductivity (EC) and superoxide anion radical (O2(*-)) values in the M. aeruginosa culture fluid increased significantly, indicating that the allelochemicals released from the root of P. stratiotes inhibited algae growth by affecting the PC and PC/APC levels in photosynthesis, destroying the cell membrane, and increasing O2(*-) content to result in oxidative damage of M. aeruginosa.
“…Without any external interference, the extracellular concentration of algal toxins was very low and negligible during the early culture stage of algal cells and remained at a relatively low level prior to the stable growth stage (Robillot et al 2000), lower than the maximum limit of 1 μg L −1 in drinking water suggested by the World Health Organization (Codd et al 2005;Umehara et al 2012). However, the application of chemical algae-killing reagents causes the death and disruption of algal cells, or the cells being inactive and lysis, leading to a substantial release of intracellular algal toxins (Daly et al 2007;Xiao et al 2010).…”
Section: Extracellular Mcs Release Affected By Artemisinin Sustained-mentioning
To safely and effectively apply artemisinin sustained-release granules to control and prevent algal water-blooms, the effects of artemisinin and its sustained-release granules on freshwater alga (Scenedesmus obliquus (S. obliquus) and Microcystis aeruginosa (M. aeruginosa)), as well as the production and release of microcystins (MCs) were studied. The results showed that artemisinin sustained-release granules inhibited the growth of M. aeruginosa (above 95% IR) and S. obliquus (about 90% IR), with M. aeruginosa more sensitive. The artemisinin sustained-release granules had a longer inhibition effect on growth of pure algae and algal coexistence than direct artemisinin dosing. The artemisinin sustained-release granules could decrease the production and release of algal toxins due to the continued stress of artemisinin released from artemisinin sustained-release granules. There was no increase in the total amount of MC-LR in the algal cell culture medium.
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