ライフサイエンスコーパス: iodate

1 ime enabled the full conversion of iodide to iodate.

2 t the chloride enhancement is not limited to iodate.

3 ion of iopamidol, and was mainly oxidized to iodate.

4 ironment may have prevented reduction of the iodate.

5 is often fortified with potassium iodide or iodate.

6 or after intraperitoneal injection of sodium iodate.

7 sponse to treatment with the oxidant, sodium iodate.

8 E) cells with a systemic injection of sodium iodate.

9 itted to intraperitoneal injection of sodium iodate (2% NaIO3, 50 mg/kg).

10 series of new alkali-metal or Tl(+) titanium iodates, A(2)Ti(IO(3))(6) (A = Li, Na, K, Rb, Cs, Tl).

11 ar calibration for iodine using a mixture of iodate and iodide ions was obtained from 10 to 100 ug L(

12 termined by combining the peak areas of both iodate and iodide ions.

13 method had a linear range 0.04-10 mg kg(-1) iodate and limit of detection of 4.4 ug kg(-1).

14 tive separation of two small inorganic ions, iodate and nitrate, is demonstrated on a reverse phase c

15 igation of POA decay and DBP (e.g., bromate, iodate, and iodophenol) generation in the POA/halide sys

16 yield HIO(3), which also contributes to the iodate anion signal.

17 We estimate that ~50% of the iodate anion signals observed by nitrate CIMS under atmo

18 lar to those obtained by CIMS, including the iodate anion.

19 This rotation allows for the iodate anions to bridge the molybdenum oxide chains in a

20 ordinate Bk(III) cations that are bridged by iodate anions to yield layers that are isomorphous with

21 molybdenum oxide chains that are bridged by iodate anions.

22 s, but results on (129)I species (iodide and iodate) are limited and only available for surface water

23 he results expose </=10% annual reduction of iodate as (129)I is transported from the English Channel

24 database entries to identify phosphates and iodates as the next generation of chemical spaces for st

25 od is presented that successfully determines iodate, chlorite, and bromate in drinking water at pract

26 Ag4(UO2)4(IO3)2(IO4)2O2 versus other uranyl iodate compounds with endotherms at 479 and 494 degrees

27 Similarly, the iodate concentrations decrease as a function of time in

28 Nevertheless, iodate concentrations decreased after a maximum was reac

29 red spectroscopy (DRS-FTIR) was employed for iodate determination in food grade salt and food product

30 e application of electrochemical methods for iodate determination was investigated using a bare scree

31 Iodate does not adsorb to the CuO surfaces used in this

32 After sodium iodate exposure, intraretinal manganese uptake was super

33 of nutrition and infection, use of potassium iodate for fortifying crude moist salt, research in the

34 of (129)I, while stable (127)I was mainly in iodate form, reflecting the fact that the major source o

35 The kinetics and the yield of iodate formation in natural waters depend mainly on the

36 The kinetics of iodate formation is a critical factor in mitigation of t

37 In this reaction system, iodate formation rates increase with increasing CuO (0-0

38 mide not only enhances the yield and rate of iodate formation, it also increases the formation of bro

39 alkaline permanganate for mineralization and iodate formation.

40 n also increased the conversion of iodide to iodate: from 45 to nearly 90% with a bromide concentrati

41 rticularly in higher iodine regions, whereas iodate impacts on thyroid risks in presence of universal

42 ficantly enhances the oxidation of iodide to iodate in a bromide-catalyzed process.

43 e quantifies 0.8-15 ppm of iodine atoms from iodate in aqueous solutions.

44 was developed for the on-site measurement of iodate in food-grade salt.

45 method was efficiently applied to determine iodate in table salt samples with percentage relative re

46 latform for electrochemical determination of iodate in table salt, offering potential as the basis fo

47 te in bottled water as well as low levels of iodate in tap water.

48 xidation reaction of tartrazine by potassium iodate in the acetate buffer medium.

49 unt of atmospherically nonrecyclable iodine (iodate) in marine aerosol.

50 Recoveries of spiked iodine (as iodate) in the samples were greater than 90%.

51 ging Pgam5(-/-) mice are resistant to sodium iodate-induced RPE cell death.

52 RPE damage was also induced by sodium iodate injection (40 mg/kg) into wild-type or albino C57

53 immobilization of aqueous iodide (I(-)) and iodate (IO(3)(-)) in the environment, but molecular inte

54 ly enriched in iodine, mostly in the form of iodate (IO(3)(-)) ions, compared to its relative abundan

55 organic (bromide (Br(-)), iodide (I(-)), and iodate (IO(3)(-))), organic, and total bromine (Br(T)) a

56 The formation rate of iodate (IO3(-)) in the CuO-HOCl-I(-) system significantl

57 e of hypoiodous acid (HIO), iodite (IO2(-)), iodate (IO3(-)), triiodide (I3(-)), and molecular iodine

58 Iodine, as an iodate ion or iodide ion, was simultaneously extracted a

59 of I(2)O(3) leads to the rapid formation of iodate ions (IO(3)(-)), which is the predominant soluble

60 Iodate ions produce a blue-black coloration on the PAD,

61 LLME), was proposed for the determination of iodate ions.

62 It could be demonstrated that iodate is oxidized to periodate by a CuO-activated hypoh

63 Because particulate iodate is readily reduced, recycling iodine back into th

64 e in the concentration range of 10 to 100 mg iodate kg(-1) of salt, and a detection limit of 2.20 mg

65 mental data about the stability of potassium iodate (KIO(3)) or iodine uptake during food processing

66 /per one plant/one application) of potassium iodate (KIO(3)), salicylic acid (SA) alone or together w

67 alues for all samples, except when potassium iodate (KIO3) was used in the recipe.

68 Three new molybdenyl iodates, KMoO3(IO3) (1), RbMoO3(IO3) (2), and CsMoO3(IO3

69 uranium oxide ribbons are joined by bridging iodate ligands to yield two-dimensional undulating sheet

70 ished and extensively characterized a sodium iodate (NaIO(3))-induced model of GA in pigmented Long E

71 Using an animal model of sodium iodate (NaIO(3))-induced RPE degeneration, BMCs were mob

72 Distribution of iodide and iodate of both (127)I and (129)I in the Kattegat mainly

73 -arylimino-3H-indolizin-4-ium-1-olates by an iodate-promoted multicomponent reaction between 3,3-difl

74 Our data suggest that iodate reduction to form volatile iodine species is a mi

75 dation of methane, ethane, and propane using iodate salts with catalytic amounts of chloride in proti

76 The reduction process of iodate seems to be related to decomposition of organic m

77 A rapid, precise, and accurate amperometric iodate sensing strategy was established with this SPCE.

78 We added potassium iodate to irrigation water over a 2 to 4 week period beg

79 Sodium iodate-treated rats exhibited an eightfold increase (P <

80 n urethane-anesthetized control rats, sodium iodate-treated rats, rats receiving intravitreally injec

81 Furthermore, in iodate-treated rats, the average vitreous signal enhance

82 When RPE cells were compromised with sodium iodate, tumor cells or ovalbumin injected into the subre

83 The reaction of (249)Bk(OH)4 with iodate under hydrothermal conditions results in the form

84 Iodate was the dominant species and accounted for up to

85 Iodate was the main species incorporated into calcite an

86 correlated with the conversion of iodide to iodate, which increased from 10 to nearly 90%.

87 (3)(-) values suggest effective reduction of iodate with a maximum rate of 8 x 10(-7) ((127)IO(3)(-))

88 confirmed the electrocatalytic reduction of iodate, yielding a sensitivity of -0.596 muA/(mg/L).