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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.
14 Biomagnification occurred during the pre algal bloom and algal bloom phases but appeared to be ab
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
19 cated in key ecological phenomena (including algal blooms and diel vertical migration) that shape the
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
30 poxia, disease outbreaks and toxin-producing algal blooms are all possible causes of mass mortality e
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.
36 Pond slime is a problem in garden pools, algal blooms can produce toxins that incapacitate or kil
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
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
52 brevetoxins (PbTxs), produced by the harmful algal bloom (HAB) species Karenia brevis, are essential
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
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
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
74 ude an example of how compounds from harmful algal blooms may yield both tools for measuring environm
76 d in proximity to the sea concomitantly with algal blooms of Ostreopsis spp. in the Mediterranean are
78 ecrease in snow albedo by red pigmented snow algal blooms over the course of one melt season can be 1
80 tion occurred during the pre algal bloom and algal bloom phases but appeared to be absent during the
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
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
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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