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1 s axial diaqua species [FeL(H 2O) 2] (-) ( 1 aqua) which are deprotonated to afford [FeL(OH)(H 2O)] (
2                               The pathways 1 aqua + H 2O 2 ( k 1), 1 OH + H 2O 2 ( k 2), and 1 OH + H
3 m based on the [Mo(2)O(2)S(2)(OH(2))(6)](2+) aqua cation (noted L) and the trivacant [AsW(9)O(33)](9-
4  was converted into the catalytically active aqua counterpart by a ligand exchange process.
5 r drug, and its related biologically active "aqua" compounds in biofluid samples is described.
6 es using a lithium borate fusion although an aqua regia leachate is also effective in many instances.
7 ive photosubstitution of the thioether by an aqua ligand.
8 ter activation with light, the release of an aqua ruthenium(II) complex is observed.
9 ich forms a hydrogen-bonding network with an aqua ligand on iron and the pterin cofactor.
10 n atom transfer from a W(IV) species with an aqua ligand, yielding W(V)-[OH(-)] and a substrate radic
11                      Monodentate acetate and aqua ligands lend the flexible environment of 1 closest
12 hich can substitute components of animal and aqua feeds.
13 nalyses were consistent with cysteinate- and aqua-ligated heme iron in CYP51.
14 enes (Bmal1, Clock, Per1, and Per2), ion and aqua channel genes (Ae2a, Car2, and Aqp5), and salivary
15                A weakly associated S-Met and aqua are likely axial ligands.
16 stems thus far, as they retain their form as aqua complexes.
17 dinated Fe(III)-TAML complexes with an axial aqua ligand ([PPh(4)]1-H(2)O, tetraamidato macrocyclic F
18  conditions to produce the corresponding bis-aqua-iron(III) porphyrin cation radicals.
19 eling agent to coordinate with the cisplatin-aqua complex.
20 8)F-FPMA for coordination with the cisplatin-aqua complex.
21                                Applying cold aqua trap-isotope ratio mass spectrometry, we discovered
22 e developed a novel methodology we call cold aqua trap-isotope ratio mass spectrometry, which allows
23  indicates the presence of a solvent-derived aqua/hydroxo ligand bound either terminally or in a brid
24          Here we show with three-dimensional aqua-planet simulations that CO2-induced forcing as read
25 NWs screening platform in real environmental aqua system.
26 as the processes that govern the equilibrium aqua-hydroxo (O2H3)(-)<-->hydroxyl (OH) in Sc-MOFs, are
27 edox-inactive Ca(2+) analogues with flexible aqua-/acetate ligands into active and stable WOCs (max.
28 or monitoring non-ruminant PAPs intended for aqua feed.
29 rom aqueous acidic solutions, including from aqua regia solutions of electronic waste.
30 2 cores having one single atom bridge (e.g., aqua or hydroxo) together with one or two carboxylate br
31  of NU-1000-supported bimetallic-oxo,hydroxo,aqua clusters.
32            Even with the less stable hydroxo/aqua complex [Cp*(2)Ir(2)(mu-OH)(3)]OH, nanoparticle for
33  structure of the axial region of the Pd(II) aqua ion in solution using a combination of neutron and
34 ssociation free energy of a resulting Ni(II)-aqua species was estimated to be 96.6-100.3 kcal mol(-1)
35                   The six-coordinate Fe(III)-aqua complex [Fe(III)(dpaq)(H2O)](2+) (1, dpaq is 2-[bis
36 rmore, in some cases, gene annotation and in aqua assays disagree by describing gene annotation witho
37  amounts of free steroids can be detected in aqua as low as; 0.17 ng/uL, 0.039 ng/uL, 0.43 ng/uL, 0.0
38 ruminant processed animal proteins (PAPs) in aqua feed, two immunoassays have been tested in an inter
39  decomposition by means of solubilisation in aqua regia or tetramethyl ammonium hydroxide and simple
40 O2, partial decomposition (solubilisation in aqua regia), 1:1 dilution with 2% (v/v) HNO3 and direct
41 tic assessment of non-conjugated steroids in aqua.
42 y porous MOF material reported to survive in aqua regia.
43 be the iron photoreactivity in terms of iron-aqua and oxalate complexes, are not in accordance with o
44                       Using the pKa of the M-aqua complex as a measure of Lewis acidity, these compou
45 drogen bonding interaction between the metal aqua and boron hydroxide moieties.
46     With the pKa of the redox-inactive metal-aqua complex as a measure of Lewis acidity, these compou
47    (2) Proton transfer from the terminal MnA-aqua ligand to the substrate Ndelta-guanidino atom forms
48 accompanied by protonations to afford the Mo-aqua complex, [(PY5Me(2))Mo(OH(2))](+).
49 (1)H ENDOR measurements indicate there is no aqua (HxO) ligand bound to the Cu(II), either terminally
50 zolyl)alkane ligands on the rate constant of aqua ligand substitution of ruthenium(II) complexes with
51 roton-coupled electron transfer oxidation of aqua precursors, but access at inert electrodes is kinet
52  process, specifically the transformation of aqua cobalt (II) complexes to their fully halogenated sp
53 igand environment of three nitrogens and one aqua ligand "in the plane".
54 sfer follows to yield a Ru(V)/Ru(III) peroxo/aqua mixed valence complex, which performs the third red
55 istidine and is likely trans to the in-plane aqua ligand.
56 ed water in any system, including the simple aqua ion.
57  cob(III)alamins bound to MetH, specifically aqua-, methyl-, and n-propylcobalamin, show a correlatio
58 magnetically coupled Ru(IV)/Ru(III) superoxo/aqua species is predicted, which will then promote the l
59 he third redox reaction to give the superoxo/aqua complex.
60  Thus, we confirm that X contains a terminal aqua (most likely hydroxo) ligand to Fe(III) in addition
61 ambiguous for Mn(IV)PFOM where both terminal aqua and hydroxo ligands can be rationalized, but the re
62 rm that X contains an Fe(III)-bound terminal aqua ligand (H(x)O), but the spectra contain none of the
63 hat Mn(II)PFOM and Mn(III)PFOM have terminal aqua ligands and Mn(V)PFOM has a terminal hydroxo ligand
64                                      Ternary aqua complexes are directly observed in the mass spectru
65                     The formation of ternary aqua complexes of metal-based diagnostics and therapeuti
66                                          The aqua complexes [[Tp(Bu)t(,Me)]M(OH(2))][HOB(C(6)F(5))(3)
67  A metal-organic framework (MOF) bearing the aqua-hydroxo species (O2H3)(-) in the framework, as well
68 y be viewed as analogous to that between the aqua ligand and Thr-199 at the active site of carbonic a
69 als; Ln(solv)n3+, where in 1:9 D2O-CD3CN the aqua complexes are the predominant species, Ln = lanthan
70  chemically functionalized; for example, the aqua ligands can be replaced by pyridines.
71  films of TiO(2) nanoparticles on glass, the aqua complex [Ru(II)(tpy)(bpy(PO(3)H(2))(2))(OH(2))](2+)
72 t irradiation enhances the production of the aqua adducts in which eq CH3CN is replaced by H2O molecu
73 determine the relative MS/MS response of the aqua compounds for the first time.
74 l ions studied, we identify the pK(a) of the aqua ion as the factor that determines the functional co
75 uo or above 383 K resulted in removal of the aqua ligands and concomitant transformation to nonporous
76  H2O molecules, whereas the formation of the aqua species for cis-[Rh2(fhp)2(CH3CN)6][BF4]2 (7) is on
77 ither can be prepared by pretreatment of the aqua-coordinated polyoxometalates (L = H2O) with NO2 or
78 thermodynamically easier to oxidize than the aqua precursor, [Mn(2+)(OH(2))].
79  that an intramolecular hydrogen bond to the aqua ligand can reduce this internal rotation and increa
80 onated by (C(6)F(5))(3)B(OH(2)) to yield the aqua derivative [[Tp(Bu)t(,Me)]Co(OH(2))][HOB(C(6)F(5))(
81 onated by (C(6)F(5))(3)B(OH(2)) to yield the aqua derivative [[Tp(Bu)t(,Me)]Zn(OH(2))][HOB(C(6)F(5))(
82 erties, both the (hydroxo)iron(III) and the (aqua)iron(II) complex reflect well the only two essentia
83 ctivity of 1 increases with pH value through aqua ligand deprotonation.
84 udies, and the latter confirms oxo and trans aqua (H2O) ligands on Au.
85  a series of tricopper hydroxo and tricopper aqua complexes as synthetic models of the tricopper site
86 minent sites of reactivity by the Cp*Rh tris aqua complex.
87              The metal is coordinated by two aqua ligands, two histidines (5 and 74), and two glutama
88 mples between 101% and 106% were found using aqua regia treatment.
89 m was simply released by acid leaching using aqua regia from environmental solid samples and preconce
90 stion, which additionally were compared with aqua regia digestion, showing inadequacies in the perfor
91        It was found that the extraction with aqua regia provides the best results, i.e., limits of de