1. Hydroxide, Ammonium
1. 1336-21-6
2. Ammonia Aqueous
3. Ammonium Hydroxide ((nh4)(oh))
4. Ammonium Hydroxide Solution
5. Ammoniumhydroxid
6. Nh4oh
7. Aquammonia
8. Ammonia, Aqua
9. Household Ammonia
10. Ammonia, Aqueous Solution
11. Ammonia, Monohydrate
12. Ammonia Water 29%
13. Caswell No. 044
14. Sx 1 (ammonia Water)
15. Ammoniumhydroxide
16. Mfcd00066650
17. Ammonia, Aqueous
18. Sx 1
19. Ammonia Water [jan]
20. Hsdb 5125
21. Einecs 215-647-6
22. Un2672
23. Un3318
24. Epa Pesticide Chemical Code 005301
25. Ammoniaque
26. Ammonia Hydrate
27. Water Ammonia
28. Ammonium Hydoxide
29. Ammonium Hydroxid
30. Ammonium Hyroxide
31. Amonium Hydroxide
32. Agua De Amoniaco
33. Ammonium Hydorxide
34. Amrnonium Hydroxide
35. Hidroxido De Amonio
36. Nh3 Water
37. Water Nh3
38. Hydroxyde D'ammonium
39. Un2073
40. Ammonia Water (tn)
41. Ammonium Aqueous (28% Or Less Nh3)
42. Amine Hydrate
43. Ammonium Hydroxide (28% Or Less Ammonia)
44. Ammonia Water (jp17)
45. Ec 215-647-6
46. Nh3 H2o
47. Nh3-h2o
48. Nh3.h2o
49. Ammonium Hydroxide Reagent Acs
50. Ammonium Hydroxide, 25% Nh3
51. Ammonia (ammonium Hydroxide) 28% By Weight Or More Nh3
52. Dtxsid4020080
53. Chebi:18219
54. Ammonium Hydroxide, 28% Solution
55. Akos015903971
56. Akos030228272
57. E527
58. Ft-0622304
59. Ammonium Hydroxide, 10% V/v Aqueous Solution
60. Ammonium Hydroxide, 50% V/v Aqueous Solution
61. Ammonium Hydroxide, 0.1n Standardized Solution
62. Ammonium Hydroxide, 1.0n Standardized Solution
63. Ammonium Hydroxide, 5.0n Standardized Solution
64. C01358
65. D04594
66. Ammonium Hydroxide, Solution 28-30% Acs Reagent
67. J-006420
68. Ammonium Hydroxide, Environmental Grade, 20-22% Nh3
69. Ammonium Hydroxide, Solution 14-16% W/w Trace Metals Grade
70. Ammonia Solution, Relative Density <0.880 At 15 Degree C In Water, With >50% Ammonia
71. Ammonium Hydroxide, Acculute Standard Volumetric Solution, Final Concentration 0.1n
72. Ammonia Solution, Relative Density <0.880 At 15 Degree C In Water, With >50% Ammonia [un3318] [nonflammable Gas, Poison Gas]
73. Ammonia Solutions, Relative Density <0.880 At 15 C In Water, With >35% But Not >50% Ammonia
74. Ammonia Solutions, Relative Density <0.880 At 15 C In Water, With >35% But Not >50% Ammonia [un2073] [nonflammable Gas]
75. Ammonia Solutions, Relative Density Between 0.880 And 0.957 At 15 C In Water, With >10% But Not >35% Ammonia
76. Ammonia Solutions, Relative Density Between 0.880 And 0.957 At 15 C In Water, With >10% But Not >35% Ammonia [un2672] [corrosive]
Molecular Weight | 35.046 g/mol |
---|---|
Molecular Formula | H5NO |
Hydrogen Bond Donor Count | 2 |
Hydrogen Bond Acceptor Count | 1 |
Rotatable Bond Count | 0 |
Exact Mass | 35.037113783 g/mol |
Monoisotopic Mass | 35.037113783 g/mol |
Topological Polar Surface Area | 2 Ų |
Heavy Atom Count | 2 |
Formal Charge | 0 |
Complexity | 0 |
Isotope Atom Count | 0 |
Defined Atom Stereocenter Count | 0 |
Undefined Atom Stereocenter Count | 0 |
Defined Bond Stereocenter Count | 0 |
Undefined Bond Stereocenter Count | 0 |
Covalently Bonded Unit Count | 2 |
10% ammonia water as a reflex respiratory stimulant; MEDICATION (VET): externally on bites & stings; As rubefacient on bruises, sprains; Inhalant; Internally as an antacid & carminative /Ammonia water-10%/
The Merck Index. 10th ed. Rahway, New Jersey: Merck Co., Inc., 1983., p. 74
... EXCRETION IS PRIMARILY BY WAY OF KIDNEYS, BUT A NOT INSIGNIFICANT AMT IS PASSED THROUGH SWEAT GLANDS.
Clayton, G.D., F.E. Clayton (eds.) Patty's Industrial Hygiene and Toxicology. Volumes 2A, 2B, 2C, 2D, 2E, 2F: Toxicology. 4th ed. New York, NY: John Wiley & Sons Inc., 1993-1994., p. 760
... Ammonium toxicity induced by ammonium acetate administration in frogs led to variable excretion of ammonia and urea into the medium. When 11.45 mM/kg body wt of ammonium acetate was administered, ammonia excretion increased while urea excretion decreased. When 4.17 mM/kg body wt of ammonium acetate was administered, the urea excretion increased while NH3 excretion decreased.
Neeraja P, Swami KS; Indian J Physiol Pharmac 27 (2): 123-8 (1983)
Ammonium hydroxide penetrates fastest, followed by sodium hydroxide, potassium hydroxide, and finally calcium hydroxide.
Sullivan, J.B. Jr., G.R. Krieger (eds.). Hazardous Materials Toxicology-Clinical Principles of Environmental Health. Baltimore, MD: Williams and Wilkins, 1992., p. 433
Male rats gavaged with 1000 umol (15)N-ammonium chloride each day for 5 days excreted low, but significant amounts of excess (15)N-NO3- in urine on the 5 days of treatment & on the 5 subsequent days. An in vitro chemical model system was used to demonstrate that oxidation of ammonia to NO3- by the hydroxyl radical at physiological pH is chemically feasible. These results are consistent with the hypothesis that ammonia is oxidized to NO3- in vivo by a nonenzymic process which involves active O species such as the hydroxyl radical.
PMID:6690089 Saul RL, Archer MC; Carcinogenesis 5 (1): 77-81 (1984)
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