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1 AgNO3 and PVP-AgNP exposed fish had common and distinct
2 AgNO3 inhibited ligand binding to adrenergic receptors a
3 kyl analogues using a sequence involving (1) AgNO3-mediated hydroxymethyl radical addition to 1,8-nap
4 the influent wastewater (ENM biosolids), (2) AgNO3, Zn(SO4)2, and micron-sized TiO2 (dissolved/bulk m
5 cophilic, was 8 times less than that in 0.5% AgNO3 and 5 times lower than that in silver sulfadiazine
7 d to kill S. aureus at the same rate as 0.5% AgNO3, with zero colonies on an agar plate, and about 6
8 hus obtained are further functionalized by a AgNO3 /Selectfluor-mediated coupling of the BPin and cya
11 to UV radiation, silver nitrate (AgNO3), and AgNO3/citrate deposited from aqueous solutions and suspe
12 xposure in experimental microcosms, AgNP and AgNO3 inhibited respiration and photosynthesis of periph
14 ompared bactericidal activities of AgNPs and AgNO3 in those bacteria commonly associated with clinica
15 avity after intranasal delivery of AgNPs and AgNO3 to mice, and characterized tissue distribution of
16 e, citrate, dexpanthenol, and carbonate) and AgNO3 on the photosynthesis of the freshwater algae Chla
17 allenes which undergo N-Boc deprotection and AgNO3-promoted cyclization to afford N-alkyl-3-pyrroline
18 d stabilities of the three nanoparticles and AgNO3 (ionic Ag) in soil were examined at three differen
19 tion of ICHO to ICOOH in both nontreated and AgNO3-treated leaves, whereas CYP71B6 is relevant for IC
22 nts amended with AgNP-citrate, AgNP-PVP, and AgNO3 was AgCl (50-65%) > Ag2S (32-42%) > Ag metal (Ag0)
24 nfluent (control); bulk/ionic TiO2, ZnO, and AgNO3 added to influent (bulk/dissolved treatment); or A
25 rs to the noncompetitive ethylene antagonist AgNO3 via the culture medium resulted in a dose-dependen
26 and 49 nm) to ionic silver (Ag(+); added as AgNO3), a historically problematic contaminant with know
27 ic and citrate coated AgNPs as well as Ag as AgNO3 were fed into sequencing batch reactors (SBRs) ino
28 lver nanoparticles and silver ions (dosed as AgNO3) on five functional end points reflecting communit
30 arge as or larger than the positive control, AgNO3, added at 4-fold the Ag concentration of the silve
35 O-cyclized product in the presence of Au(I)/AgNO3 and N-cyclized product in the presence of Au(I)/Ag
38 stration of AgNPs versus soluble silver ion (AgNO3) control to examine their transport and biological
39 ECL) technology coupled with silver nitrate (AgNO3) enhancement in acetonitrile at a platinum electro
40 ilver nanoparticles (nAg) or silver nitrate (AgNO3) has been shown to improve the microbiological eff
41 ia exposure to UV radiation, silver nitrate (AgNO3), and AgNO3/citrate deposited from aqueous solutio
42 HT3R subunit, both MTSET and silver nitrate (AgNO3), another cysteine-modifying reagent, significantl
43 omposition in nontreated and silver nitrate (AgNO3)-treated leaf tissue was comprehensively analyzed.
49 Silver colloids synthesized by reduction of AgNO3 by trisodium citrate were used as SERS-active subs
52 painted with 0.03 mg/g casein-coated nAg or AgNO3 were measured as a function of pH (5-9), ionic str
53 both in medium and in nematodes) and rescued AgNO3- and CIT-Ag NP-induced cellular damage, potentiall
57 rimethylammonium chloride (CTAC) surfactant, AgNO3, ascorbic acid, and NaOH to form the core-shell na
58 ne derivative is selectively retained by the AgNO3-impregnated silica, but the cis-isomer elutes from
60 ow reduced bactericidal activity compared to AgNO3 (i.e., MBC of 15ppm compared to 5ppm), and signifi
62 dase treatment revealed that, in response to AgNO3 treatment, their total accumulation level was simi
67 e, we found that HDL from mice injected with AgNO3 fails to inhibit palmitate-induced inflammation an
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