コーパス検索結果 (1語後でソート)
通し番号をクリックするとPubMedの該当ページを表示します
1 rolyze trinucleotide, even in the absence of metalloid.
2 ments, making it a major sink for this toxic metalloid.
3 ArsD at 1.4 A and a model for its binding of metalloid.
4 , as opposed to release and rebinding of the metalloid.
5 sO)(n), (SbO)(n), or a co-polymer of the two metalloids.
6 been shown to facilitate uptake of trivalent metalloids.
7 eric ArsD, with only one site releasing free metalloids.
8 quality limits, mainly with heavy metals and metalloids.
9 voltaic cells crucially depend on metals and metalloids.
10 n of the rates of binding and affinities for metalloids.
11 ing responses to toxic transition metals and metalloids.
14 of glycerol, this is the first report where metalloid and glycerol transport can be dissected by a s
15 s-172 controls the affinity of this site for metalloid and hence the efficiency of metalloactivation
18 cellular sensitivity to arsenicals and other metalloids and can modulate intracellular glutathione me
19 k because of the low concentration of metals/metalloids and the correspondingly high molecular chemic
21 ter shell electronic structure of metals and metalloids and the viscoelasticity and fragility thereof
22 Because arsenic and antimony are related metalloids, and arsenical resistant Leishmania strains a
23 amples of microbial metabolism of metals and metalloids; and expanded the types of information it inc
25 c results in cross-resistance to the related metalloid antimony, present in the pentavalent state as
26 e) minerals determines the fate of the toxic metalloid arsenic (As) in many subsurface environments.
30 obic respiration of ferric iron or the toxic metalloid arsenic is well known to affect water quality
35 ce to trivalent and pentavalent salts of the metalloids arsenic and antimony in cells of Escherichia
36 ce to trivalent and pentavalent salts of the metalloids arsenic and antimony in cells of Escherichia
39 common heavy metal contaminant lead and the metalloids arsenic and selenium in mine tailings and con
40 on H2S production and the leaching of metals/metalloids (arsenic, copper, chromium, and boron) from t
41 73 confers resistance to the toxic trivalent metalloids arsenite [As(III)] and antimonite [Sb(III)].
42 p has been shown to facilitate uptake of the metalloids arsenite and antimonite, and the Escherichia
44 Reductive release of the potentially toxic metalloid As from Fe(III) (oxyhydr)oxides has been ident
46 higher levels of the heavy metal Cd and the metalloid As, it does not increase the accumulation pote
47 e ArsAB pump that catalyzes extrusion of the metalloids As(III) and Sb(III), conferring metalloid res
51 s a metallochaperone that delivers trivalent metalloids [As(III) or Sb(III)] to the ArsA ATPase, the
53 The ArsD metallochaperone delivers trivalent metalloids, As(III) or Sb(III), to the ArsA ATPase, the
54 ave assessed the major uses of 56 metals and metalloids, assigning each use to one of three categorie
56 stal structure of ArsA shows two other bound metalloid atoms, one liganded to Cys-172 and His-453, an
59 ng a nucleotide binding domain, and a single metalloid binding or activation domain is located at the
60 422A)B in less than 1 week, showing that the metalloid binding site confers an evolutionary advantage
61 st that there is only a single high-affinity metalloid binding site in ArsA, and second that Cys-172
72 I) displacement by As(III) revealed that the metalloid-binding sites behave differentially, with the
73 nic (As) is considered the most common toxic metalloid, but its molecular mode of action is not well
74 ation of metalloid, high affinity binding of metalloid by ArsA is not obligatory for transport or res
76 ntrolling factor elucidation of toxic metals/metalloids by introducing an index, enrichment factor (E
77 olving the sequential binding and release of metalloids by the four binding sites of dimeric ArsD, wi
78 hoate >> tau-fluvalinate), then trace metals/metalloids (cadmium, arsenic), followed by the fungicide
80 In the mine impacted environment, metals and metalloids commonly coexist in a variety of species.
82 y an effective tool for evaluating metal and metalloid concentrations but can suffer from poor replic
83 sIII oxidation and AsIII/SbIII resistance at metalloid concentrations inhibitory to the Deltaacr3-1 m
86 olecular-level speciation of heavy metal and metalloid contaminants in various environmental settings
87 suggests that in addition to Hg other metals/metalloids could also potentially be an environmental pr
88 13 pair was required for the majority of the metalloid-dependent quenching of Trp-97 fluorescence.
89 r species, the formal oxidation state of the metalloid diminishes from III, to II, to I, and finally
90 ponent compounds of metals and chalcogens or metalloids, doped fullerenes and organic charge-transfer
91 This is the first report of the uptake of a metalloid drug by an aquaglyceroporin in Leishmania, sug
92 s As during crystallization and retains this metalloid during the transformation from struvite, can a
93 te and metabolism of Se (and other metal and metalloids) during anuran development and the implicatio
94 measurement site are enriched in metals and metalloids (e.g., arsenic, lead, and cadmium) and water-
95 were found to have elevated levels of metals/metalloids (e.g., mercury, arsenic, and lead) with separ
97 ance of DOM sulfurization to trace metal and metalloid (especially mercury) fate in the environment.
99 control microbiomes are suppressed by metal/metalloid field exposure, including eradication of the h
100 D to ArsA, consistent with channeling of the metalloid from one protein to the other, as opposed to r
101 nce for and accumulation of heavy metals and metalloids from soil by expressing an Arabidopsis thalia
103 to reduce the intracellular concentration of metalloid, high affinity binding of metalloid by ArsA is
106 haracterize the criticality of 62 metals and metalloids in a 3D "criticality space" consisting of sup
114 z1/Ynl155w is proposed to protect cells from metalloid-induced proteotoxicity by delivering ubiquitin
116 of genes for resistance to heavy metals and metalloids is usually transcriptionally regulated by the
117 yotes are known to grow on and respire toxic metalloids of arsenic (i.e., arsenate and arsenite).
120 (Pb), whereas greater than 97% of metals and metalloids present were associated with the glass matrix
122 A/C422A)B genes had an intermediate level of metalloid resistance and accumulation between those expr
124 us species harvested from the environment is metalloid resistant and, when grown anaerobically in com
125 in a 3.8-kb chromosomal DNA fragment from a metalloid-resistant thermophile, Geobacillus stearotherm
127 f the steady-state fluorescence of ArsD with metalloids revealed positive cooperativity, with a Hill
128 nzyme will improve our understanding of this metalloid's metabolism and its actions as a toxin and a
131 uptake of As(III) or Sb(III) correlated with metalloid sensitivity of the wild type and drug-resistan
133 n exhibited varying levels of both basal and metalloid-stimulated activity, indicating that neither A
136 P]-triphosphate at 4 degrees C indicate that metalloid stimulation correlates with a >10-fold increas
143 entially form separate binding sites for the metalloids that trigger dissociation of ArsD from the op
144 esistance is proposed to be formation of the metalloid-thiol pump substrates, so that increased synth
147 ally, various mechanisms for heavy metal and metalloid tolerance and virulence point to a lifestyle w
149 to alanine, aspartate and glutamine affected metalloid transport in the order, wild-type > E152Q > E1
151 (MDR)-1 is the key factor in the failure of metalloid treatment in kala-azar patients infected with
153 may help better understand the mechanisms of metalloid uptake, tolerance and detoxification in plants
158 c is a ubiquitous, naturally occurring toxic metalloid widely distributed in soil and groundwater.
159 e predominant emission source for metals and metalloids, with Cd released to such extents that PEC (1
WebLSDに未収録の専門用語(用法)は "新規対訳" から投稿できます。