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1 es but appeared to be absent during the post algal bloom.
2 pounds in contaminated water such as harmful algal blooms.
3 nd can accelerate eutrophication and harmful algal blooms.
4 itating the formation of large scale harmful algal blooms.
5 cluding the potential development of harmful algal blooms.
6 ions in regulating the occurrence of harmful algal blooms.
7 e waters impaired by wastewater effluents or algal blooms.
8  some additional mechanisms of regulation of algal blooms.
9 f available nutrients and the termination of algal blooms.
10 take up to 0.3 micromol.m(-2).s(-1) in dense algal blooms.
11 smarter bio-hydrochar materials by utilizing algal blooms.
12 s or one with potentially disruptive harmful algal blooms.
13 m is one of the main species causing harmful algal blooms along the tropical Pacific.
14     Biomagnification occurred during the pre algal bloom and algal bloom phases but appeared to be ab
15 n during the heat wave was accompanied by an algal bloom and chemically enhanced carbon uptake.
16 aquatic ecosystems with nutrients leading to algal blooms and anoxic events) is a persistent conditio
17  can be released to the water during harmful algal blooms and are a serious threat to animals and hum
18 ton, and the effect of these interactions on algal blooms and climate.
19 cated in key ecological phenomena (including algal blooms and diel vertical migration) that shape the
20 y for an early warning before occurrences of algal blooms and for environmental management.
21                              Renewed harmful algal blooms and hypoxia in Lake Erie have drawn signifi
22 educe phosphorus loading that drives harmful algal blooms and hypoxia.
23 rope and North America show that controlling algal blooms and other symptoms of eutrophication depend
24 e environment has focused primarily on toxic algal blooms and pathogenic bacteria that multiply in nu
25  and treated waters include chemical spills, algal blooms, and increased salinization, organoleptic e
26 ater, cyanobacterial cultures, extracts, and algal blooms, and may be useful in detecting metabolites
27  of the most toxic compounds produced by the algal blooms, and reveal that the degradation efficiency
28 minant sources of TONO and their precursors, algal blooms, and to a lesser degree agricultural or sto
29  a bloom-and-bust lifestyle in which massive algal blooms appear and fade.
30 poxia, disease outbreaks and toxin-producing algal blooms are all possible causes of mass mortality e
31                                 DA-producing algal blooms are increasing in size and frequency.
32 ution and reduced grazing each can stimulate algal blooms as shown by numerous experiments.
33 cteria may play a role in regulating harmful algal blooms, but little is known about the biochemical
34  for modelling outcome of grazing control of algal blooms by zooplankton in nutrient-rich ecosystems.
35                                     Postfire algal blooms can increase chlorine reactivity of fire-af
36     Pond slime is a problem in garden pools, algal blooms can produce toxins that incapacitate or kil
37                                      Harmful algal blooms cause serious problems worldwide due to lar
38                                   Brown tide algal blooms, caused by the excessive growth of Aureococ
39 ning RNA sequences from two related, harmful algal bloom-causing Alexandrium species.
40 obal proliferation of cyanobacterial harmful algal blooms (CHABs), yet we have limited understanding
41 lgal biodiversity and species distributions, algal bloom control, dimethyl sulphide formation and gen
42                       Cyanobacterial harmful algal blooms (CyanoHABs) have serious adverse effects on
43 ies and magnitudes of cyanobacterial harmful algal blooms (CyanoHABs) in freshwater systems.
44 rovides evidence for trace metal linkages in algal bloom development.
45 ing phytoplankton growth and could influence algal bloom development.
46                                              Algal-bloom dilution controlled the variability in the M
47 tion of karlotoxin 2 (KmTx2; 1), the harmful algal bloom dinoflagellate Karlodinium sp. was collected
48 plore the effects of an Ecosystem Disruptive Algal Bloom (EDAB) on the microbial community separated
49  dilution (MeHg burden per cell decreases in algal blooms), extending patterns of contaminant accumul
50 tative morphological analysis of the harmful-algal-bloom-forming raphidophyte Heterosigma akashiwo to
51               Toxins produced by the harmful algal bloom (HAB) forming, mixotrophic dinoflagellate Ka
52 brevetoxins (PbTxs), produced by the harmful algal bloom (HAB) species Karenia brevis, are essential
53                                      Harmful algal blooms (HABs) are frequently reported around the g
54 , yet the impacts of such changes on harmful algal blooms (HABs) are not fully understood.
55                                      Harmful algal blooms (HABs) cause significant economic and ecolo
56                                      Harmful algal blooms (HABs) induced by eutrophication is becomin
57                           Preventing harmful algal blooms (HABs) is needed to protect lakes and downs
58                 In freshwater lakes, harmful algal blooms (HABs) of Cyanobacteria (blue-green algae)
59    With the increase in frequency of harmful algal blooms (HABs) worldwide, a better understanding of
60 can play a central role in promoting harmful algal blooms (HABs), and therefore many HAB studies to d
61 ies, mostly dinoflagellates, causing Harmful Algal Blooms (HABs), produce toxins which may affect the
62                                      Harmful algal blooms (HABs), those proliferations of algae that
63                    The occurrence of harmful algal blooms has resulted in growing worldwide concern a
64  Lake Erie, whereas a record-setting harmful algal bloom in 2011 was likely associated with only mild
65 1, Lake Erie experienced the largest harmful algal bloom in its recorded history, with a peak intensi
66 ake, Seattle during a cyanobacterial harmful algal bloom in the summer of 2014 were studied using a n
67 long-term self-regulation of available P for algal blooming in eutrophic lakes.
68 The recent resurgence of hypoxia and harmful algal blooms in Lake Erie, driven substantially by phosp
69 erial-algal interactions, control of massive algal blooms in the ocean, and the maintenance and degra
70 that lead to the rapid demise of large-scale algal blooms in the oceans.
71  remained high, increasing the likelihood of algal blooms in warming summer temperatures.
72 arine organism often associated with harmful algal blooms known as 'red tides'.
73                                        Toxic algal blooms may involve such eco-evolutionary feedbacks
74 ude an example of how compounds from harmful algal blooms may yield both tools for measuring environm
75  amplicon sequencing as a supporting tool in algal bloom monitoring or water-resource management.
76 d in proximity to the sea concomitantly with algal blooms of Ostreopsis spp. in the Mediterranean are
77  analogues have been reported from cultures, algal blooms, or other contaminated samples.
78 ecrease in snow albedo by red pigmented snow algal blooms over the course of one melt season can be 1
79  to May, with BAFs having minima in the post algal bloom phase.
80 tion occurred during the pre algal bloom and algal bloom phases but appeared to be absent during the
81           Our results support that a harmful algal bloom producing a yessotoxin was a major causative
82 mmediately after the death of massive annual algal blooms showed that no selenomethionine or selenome
83 th the global proliferation of toxic harmful algal bloom species, there is a need to identify the env
84 sults indicate that postfire ash loading and algal bloom stage may significantly affect DBP formation
85 collected directly from Lake Erie during the algal blooms that affected 500000 residents in Toledo in
86 d top-down and bottom-up effects facilitated algal blooms that shifted ecosystem functions.
87 microbes determine the prevalence of harmful algal blooms that threaten water quality.
88 ion history, and six species causing harmful algal blooms, to determine the ecoregions most likely to
89 Here, we address this challenge and quantify algal blooms' turnover using a combination of satellite
90 no evidence of a long-term hurricane-induced algal bloom was observed.
91 rophic, selenium-impacted river with massive algal blooms, which consisted of filamentous green algae
92 enic inputs of nutrients have fueled massive algal blooms, which deplete bottom waters of oxygen (O(2

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