ライフサイエンスコーパス: algal bloom

1 regulation, effectively reducing the spring algal bloom.

2 es but appeared to be absent during the post algal bloom.

3 from episodic disturbances, such as harmful algal blooms.

4 some additional mechanisms of regulation of algal blooms.

5 f available nutrients and the termination of algal blooms.

6 take up to 0.3 micromol.m(-2).s(-1) in dense algal blooms.

7 s or one with potentially disruptive harmful algal blooms.

8 yanotoxin microcystin-LR produced by harmful algal blooms.

9 es, (2) microbial community structure during algal blooms.

10 n degradation, a prominent polysaccharide in algal blooms.

11 anobacteria and Chlorophyta mainly dominated algal blooms.

12 ing as a key biological indicator of harmful algal blooms.

13 articularly as major contributors of harmful algal blooms.

14 king management decisions related to harmful algal blooms.

15 ystems, including the development of harmful algal blooms.

16 eases the frequency and intensity of harmful algal blooms.

17 fe nature-based solution for combating toxic algal blooms.

18 induce respiratory syndromes during harmful algal blooms.

19 d lead to harmful ecological events, such as algal blooms.

20 enters the marine food chain during harmful algal blooms.

21 pounds in contaminated water such as harmful algal blooms.

22 ions in regulating the occurrence of harmful algal blooms.

23 smarter bio-hydrochar materials by utilizing algal blooms.

24 -eutrophication and it is plagued by harmful algal blooms.

25 nd can accelerate eutrophication and harmful algal blooms.

26 itating the formation of large scale harmful algal blooms.

27 cluding the potential development of harmful algal blooms.

28 e waters impaired by wastewater effluents or algal blooms.

29 Increasing occurrence of harmful algal blooms across the land-water interface poses signi

30 m is one of the main species causing harmful algal blooms along the tropical Pacific.

31 ypoxia)(1) and increases in the incidence of algal blooms.Although recent work has suggested that ind

32 ion, with peak N(SSA) during the first mixed algal bloom and a decline during the G. huxleyi bloom an

33 Biomagnification occurred during the pre algal bloom and algal bloom phases but appeared to be ab

34 ater samples were collected during a harmful algal bloom and analyzed by LC-MS with simultaneous HRMS

35 n during the heat wave was accompanied by an algal bloom and chemically enhanced carbon uptake.

36 aquatic ecosystems with nutrients leading to algal blooms and anoxic events) is a persistent conditio

37 can be released to the water during harmful algal blooms and are a serious threat to animals and hum

38 monly encountered macroalgal species forming algal blooms and are responsible for many Green Tide eve

39 ton, and the effect of these interactions on algal blooms and climate.

40 cated in key ecological phenomena (including algal blooms and diel vertical migration) that shape the

41 rimary producers in the oceans, the cause of algal blooms and endosymbionts of marine invertebrates.

42 y for an early warning before occurrences of algal blooms and for environmental management.

43 Erie has experienced a resurgence of harmful algal blooms and hypoxia driven by increased nutrient lo

44 Renewed harmful algal blooms and hypoxia in Lake Erie have drawn signifi

45 educe phosphorus loading that drives harmful algal blooms and hypoxia.

46 Ecological impacts range from harmful algal blooms and mass mortality events to reconfiguratio

47 ication or decline, particularly in areas of algal blooms and near coral reefs, as well as in areas a

48 rope and North America show that controlling algal blooms and other symptoms of eutrophication depend

49 e environment has focused primarily on toxic algal blooms and pathogenic bacteria that multiply in nu

50 Winter phytoplankton seed spring algal blooms and regulate nutrient cycling and ecosystem

51 iogeochemical environmental perturbations on algal blooms and their influence on biospheric environme

52 e fluids is important to many natural (e.g., algal blooms) and industrial (e.g., biofuel, vaccine pro

53 urbances including mass mortalities, harmful algal blooms, and declines in subtidal kelp beds.

54 and treated waters include chemical spills, algal blooms, and increased salinization, organoleptic e

55 ater, cyanobacterial cultures, extracts, and algal blooms, and may be useful in detecting metabolites

56 ts on water quality, such as eutrophication, algal blooms, and oxygen depletion.

57 of the most toxic compounds produced by the algal blooms, and reveal that the degradation efficiency

58 minant sources of TONO and their precursors, algal blooms, and to a lesser degree agricultural or sto

59 a bloom-and-bust lifestyle in which massive algal blooms appear and fade.

60 poxia, disease outbreaks and toxin-producing algal blooms are all possible causes of mass mortality e

61 These algal blooms are driven by a combination of environmenta

62 Algal blooms are hotspots of marine primary production a

63 DA-producing algal blooms are increasing in size and frequency.

64 Algal blooms are observed covering up to 2.7 km(2) (~20%

65 s, for example, the increased persistence of algal blooms as observed in our mesocosm experiment.

66 ution and reduced grazing each can stimulate algal blooms as shown by numerous experiments.

67 Here we map daily marine coastal algal blooms between 2003 and 2020 using global satellit

68 cteria may play a role in regulating harmful algal blooms, but little is known about the biochemical

69 physiological traits associated with harmful algal blooms, but the genetic basis for this variation i

70 esponse to a Karenia brevis red tide harmful algal bloom by examining sound spectrum levels recorded

71 for modelling outcome of grazing control of algal blooms by zooplankton in nutrient-rich ecosystems.

72 Postfire algal blooms can increase chlorine reactivity of fire-af

73 Pond slime is a problem in garden pools, algal blooms can produce toxins that incapacitate or kil

74 Harmful algal blooms cause serious problems worldwide due to lar

75 "Red tides" are harmful algal blooms caused by dinoflagellate microalgae that ac

76 Brown tide algal blooms, caused by the excessive growth of Aureococ

77 ning RNA sequences from two related, harmful algal bloom-causing Alexandrium species.

78 Cyanobacterial harmful algal blooms (cHABs) have the potential to adversely aff

79 ce the development of cyanobacterial harmful algal blooms (cHABs), but those biotic factors are poorl

80 obal proliferation of cyanobacterial harmful algal blooms (CHABs), yet we have limited understanding

81 lgal biodiversity and species distributions, algal bloom control, dimethyl sulphide formation and gen

82 tified in a Lake Erie cyanobacterial harmful algal bloom (cyanoHAB), using high-resolution UHPLC-MS a

83 the proliferation of cyanobacterial harmful algal blooms (cyanoHABs) and production of the hepatotox

84 Cyanobacterial harmful algal blooms (cyanoHABs) are a serious environmental, wa

85 Cyanobacterial harmful algal blooms (CyanoHABs) have serious adverse effects on

86 ies and magnitudes of cyanobacterial harmful algal blooms (CyanoHABs) in freshwater systems.

87 Cyanobacterial harmful algal blooms (CyanoHABs) pose serious risks to inland wa

88 synthetic prokaryotes, but some form harmful algal blooms (cyanoHABs) that disrupt ecosystems and pro

89 produced during some cyanobacterial harmful algal blooms (cyanoHABs), can harm ecosystems and requir

90 acteria and eukaryotes in urban lakes during algal bloom development stage (i.e., April, May, and Jun

91 phic level is lacking for urban lakes during algal bloom development stage.

92 rovides evidence for trace metal linkages in algal bloom development.

93 ing phytoplankton growth and could influence algal bloom development.

94 Algal-bloom dilution controlled the variability in the M

95 tion of karlotoxin 2 (KmTx2; 1), the harmful algal bloom dinoflagellate Karlodinium sp. was collected

96 s lowest in the central basin with recurrent algal blooms due to their shading effect and is highest

97 ngs underscore the complex interplay between algal bloom dynamics and SSA production, with implicatio

98 plore the effects of an Ecosystem Disruptive Algal Bloom (EDAB) on the microbial community separated

99 Macro-algal blooms, eutrophication, and reduction in coral cov

100 change pressures likely to influence harmful algal blooms, exposure to microcystin, a known hepatotox

101 dilution (MeHg burden per cell decreases in algal blooms), extending patterns of contaminant accumul

102 ons of DMS, HOBr, and CHBr(3) during typical algal bloom fluxes of DMS and HOBr (10(-13) to 10(-9) M

103 experiment revealed two main blooms: a mixed algal bloom followed by an extensive bloom of the coccol

104 an alleviate environmental issues, including algal bloom formation and greenhouse gas emissions from

105 need for similar resources for other harmful algal-bloom-forming morphospecies.

106 tative morphological analysis of the harmful-algal-bloom-forming raphidophyte Heterosigma akashiwo to

107 limate change is predicted to intensify lake algal blooms globally and result in regime shifts.

108 in-producing microalga, which causes harmful algal blooms globally, frequently leading to massive fis

109 nto waterbodies, initiating numerous harmful algal bloom (HAB) events, especially in fragile ecosyste

110 Toxins produced by the harmful algal bloom (HAB) forming, mixotrophic dinoflagellate Ka

111 In 2015, the largest recorded harmful algal bloom (HAB) occurred in the Northeast Pacific, cau

112 sphorus (P) loads from the MRW drive harmful algal bloom (HAB) severity in Lake Erie; hence changes i

113 brevetoxins (PbTxs), produced by the harmful algal bloom (HAB) species Karenia brevis, are essential

114 Microcystis, a common harmful algal bloom (HAB) taxon, threatens water supplies and hu

115 n (DO), decreased water clarity, and harmful algal blooms (HAB).

116 Harmful algal blooms (HABs) affect both freshwater and marine sy

117 Forecasting systems for harmful algal blooms (HABs) are becoming more common, as HAB mon

118 Harmful algal blooms (HABs) are frequently reported around the g

119 Harmful algal blooms (HABs) are increasing globally, causing eco

120 , yet the impacts of such changes on harmful algal blooms (HABs) are not fully understood.

121 Harmful algal blooms (HABs) can release cyanotoxins such as micr

122 Harmful algal blooms (HABs) cause significant economic and ecolo

123 Harmful algal blooms (HABs) caused by cyanobacteria in freshwate

124 aerosolization of toxins from marine harmful algal blooms (HABs) has been well documented, the aeroso

125 Harmful algal blooms (HABs) have become a worldwide environmenta

126 Harmful algal blooms (HABs) induced by eutrophication is becomin

127 Preventing harmful algal blooms (HABs) is needed to protect lakes and downs

128 In freshwater lakes, harmful algal blooms (HABs) of Cyanobacteria (blue-green algae)

129 Harmful algal blooms (HABs) of the toxigenic haptophyte Chrysoch

130 Harmful algal blooms (HABs) produce neurotoxins that affect huma

131 Harmful algal blooms (HABs) produce potent neurotoxins that thre

132 Harmful algal blooms (HABs) produce toxins that pose major chall

133 s is critical for early detection of harmful algal blooms (HABs) to enable efficient response by wate

134 With the increase in frequency of harmful algal blooms (HABs) worldwide, a better understanding of

135 can play a central role in promoting harmful algal blooms (HABs), and therefore many HAB studies to d

136 ies, mostly dinoflagellates, causing Harmful Algal Blooms (HABs), produce toxins which may affect the

137 Harmful algal blooms (HABs), those proliferations of algae that

138 tention on their role in stimulating harmful algal blooms (HABs).

139 rowth and give rise to the so-called harmful algal blooms (HABs).

140 oxygen, fish health treatments, and harmful algal blooms (HABs).

141 The occurrence of harmful algal blooms has resulted in growing worldwide concern a

142 Lake Erie, whereas a record-setting harmful algal bloom in 2011 was likely associated with only mild

143 1, Lake Erie experienced the largest harmful algal bloom in its recorded history, with a peak intensi

144 ake, Seattle during a cyanobacterial harmful algal bloom in the summer of 2014 were studied using a n

145 long-term self-regulation of available P for algal blooming in eutrophic lakes.

146 atersheds suggests greater potential to fuel algal blooms in coastal areas, especially given the like

147 tressors, thus weakening top-down control on algal blooms in eutrophic lakes.

148 and comprehensive assessment of the roles of algal blooms in generating fixed carbon for the food cha

149 hods with a motivating case study of sea ice algal blooms in heterogeneous environments.

150 The recent resurgence of hypoxia and harmful algal blooms in Lake Erie, driven substantially by phosp

151 encounter complex unsteady flows, including algal blooms in marine settings, microbial infections in

152 risks to populations that encounter harmful algal blooms in pre-to-postsenescent stages.

153 Algal blooms in the Alps therefore do not constitute a p

154 erial-algal interactions, control of massive algal blooms in the ocean, and the maintenance and degra

155 that lead to the rapid demise of large-scale algal blooms in the oceans.

156 remained high, increasing the likelihood of algal blooms in warming summer temperatures.

157 redictive biomarkers for forecasting harmful algal bloom initiation, potentially mitigating detriment

158 arine organism often associated with harmful algal blooms known as 'red tides'.

159 rence of multiple types of extremes, notably algal blooms, lake heatwaves, and low lake levels, have

160 Toxic algal blooms may involve such eco-evolutionary feedbacks

161 ude an example of how compounds from harmful algal blooms may yield both tools for measuring environm

162 In harmful algal bloom mitigation scenarios, the clustered ANN mode

163 Modelling key parameters in the algal bloom model as random variables changes the timing

164 niques to help understand the dynamics of an algal bloom model with random parameters.

165 amplicon sequencing as a supporting tool in algal bloom monitoring or water-resource management.

166 nce data set collected during the spring ice-algal bloom near Utqiagvik, Alaska in 2021 to study sea-

167 We found that algal blooms occurred in 126 out of the 153 coastal coun

168 ase whereas snowmelt duration, that controls algal blooms' occurrences, is less sensitive to global t

169 d in proximity to the sea concomitantly with algal blooms of Ostreopsis spp. in the Mediterranean are

170 Harmful algal blooms of the toxic haptophyte Prymnesium parvum a

171 presence, diversity and bioalbedo effects of algal blooms on Antarctic ice cap systems based on field

172 as attributed to a persistent Karenia brevis algal bloom or 'red tide' centered in Southwest Florida.

173 analogues have been reported from cultures, algal blooms, or other contaminated samples.

174 Phenomena like lake eutrophication, algal blooms, or reorganization in community composition

175 itiation, potentially mitigating detrimental algal bloom outcomes in the future.

176 ecrease in snow albedo by red pigmented snow algal blooms over the course of one melt season can be 1

177 The ice-algal bloom peaked on May 8th, reaching 46.6 mg chloroph

178 to May, with BAFs having minima in the post algal bloom phase.

179 tion occurred during the pre algal bloom and algal bloom phases but appeared to be absent during the

180 Algal blooms play important roles in physical and biolog

181 Harmful algal blooms present severe environmental threats, impac

182 se changes are predicted to increase harmful algal bloom prevalence and toxicity, as rising temperatu

183 Our results support that a harmful algal bloom producing a yessotoxin was a major causative

184 80% relative abundance), coincided with the algal bloom raising questions about hydrocarbon exposure

185 vailability of Fe(EPS) in AS inoculums-after algal bloom-selects cyanobacteria, and the limitation of

186 mmediately after the death of massive annual algal blooms showed that no selenomethionine or selenome

187 th the global proliferation of toxic harmful algal bloom species, there is a need to identify the env

188 sults indicate that postfire ash loading and algal bloom stage may significantly affect DBP formation

189 Much of the evolutionary ecology of toxic algal blooms (TABs) remains unclear, including the role

190 eriences annual red tides, a type of harmful algal bloom that results from high concentrations of Kar

191 collected directly from Lake Erie during the algal blooms that affected 500000 residents in Toledo in

192 Algal blooms that contaminate freshwater resources with

193 presents the first iRF application to marine algal blooms that helps to identify ocean, microbial, an

194 sota, USA suffers from recurring late summer algal blooms that often contain toxin-producing cyanobac

195 d top-down and bottom-up effects facilitated algal blooms that shifted ecosystem functions.

196 microbes determine the prevalence of harmful algal blooms that threaten water quality.

197 ritical research is needed regarding harmful algal blooms threatening ecosystem and human health, esp

198 om cultural eutrophication including harmful algal blooms, threatening both ecosystem and public heal

199 ion history, and six species causing harmful algal blooms, to determine the ecoregions most likely to

200 ation between exposure to the common harmful algal bloom toxin microcystin and the altered host gut m

201 Here, we address this challenge and quantify algal blooms' turnover using a combination of satellite

202 t MeHg increases associated with intensified algal blooms under warming.

203 The sea-ice algal bloom was dominated by diatoms, particularly, Nitz

204 no evidence of a long-term hurricane-induced algal bloom was observed.

205 on local fisheries, proliferation of harmful algal blooms, water clarity, and submerged aquatic veget

206 roach to samples collected during an induced algal bloom, which enabled pairing active giant viruses

207 rophic, selenium-impacted river with massive algal blooms, which consisted of filamentous green algae

208 enic inputs of nutrients have fueled massive algal blooms, which deplete bottom waters of oxygen (O(2

209 ising temperatures increase the frequency of algal blooms, which often have negative effects such as

210 o linked to eutrophication and the spread of algal blooms with an increasing economic and environment

211 ning a critical nursery habitat into harmful algal blooms with catastrophic impacts on coastal ecosys

212 number concentration (N(SSA)) during induced algal blooms within three airtight mesocosm enclosures.