Results for:
Species: Pseudoalteromonas sp.

Iodomethane

Mass-Spectra

Compound Details

Synonymous names
IODOMETHANE
Methyl iodide
74-88-4
Monoiodomethane
Methane, iodo-
Methyljodid
Jod-methan
Methyliodide
Methyl iodine
Methyljodide
Iodometano
Joodmethaan
Metylu jodek
Iodure de methyle
CH3I
Monoioduro di metile
Halon 10001
Methyliodid
iodo-methane
RCRA waste number U138
Monoiodmethan
Iodmethan
iodo methane
NSC 9366
DAT010ZJSR
IODOMETHANE-13C-D3
CHEBI:39282
NSC-9366
MFCD00001073
MEI
Joodmethaan [Dutch]
Iodometano [Italian]
Methyljodid [German]
Methyljodide [Dutch]
Jod-methan [German]
Metylu jodek [Polish]
Iodure de methyle [French]
CCRIS 395
Monoioduro di metile [Italian]
HSDB 1336
EINECS 200-819-5
UNII-DAT010ZJSR
UN2644
RCRA waste no. U138
iodmethane
iodometane
iodomethan
iodornethane
methiodide
methyliodine
carbon-iodine
mehyl iodide
methy iodide
metyl iodide
Methyl-iodide
meth-yl iodide
1-iodomethane
ICH3
EC 200-819-5
METHYL IODIDE [MI]
METHYL IODIDE [HSDB]
METHYL IODIDE [IARC]
WLN: I1
CHEMBL115849
DTXSID0024187
Iodomethane, ampule of 100 mg
DTXSID60167860
InChI=1/CH3I/c1-2/h1H
NSC9366
BCP26570
BBL034228
Iodomethane, for synthesis, 99.0%
STL281179
AKOS009031541
Methyl iodide [UN2644] [Poison]
MCULE-1718786667
UN 2644
Iodomethane, purum, >=99.0% (GC)
Iodomethane contains copper as stabilizer
BP-11384
Iodomethane, SAJ first grade, >=93.0%
Iodomethane, SAJ special grade, >=99.5%
I0060
NS00001340
C18448
Iodomethane, puriss., redist., >=99.5% (GC)
Q421729
F2190-0170
Iodomethane, contains copper as stabilizer, ReagentPlus(R), 99%
Iodomethane, contains copper as stabilizer, ReagentPlus(R), 99.5%
Iodomethane, 2000 mug/mL in methanol: water (4:1), analytical standard
Iodomethane, 2M soln. in tert-butyl methyl ether (stabilized with Cu)
Microorganism:

Yes

IUPAC nameiodomethane
SMILESCI
InchiInChI=1S/CH3I/c1-2/h1H3
FormulaCH3I
PubChem ID6328
Molweight141.939
LogP1.5
Atoms2
Bonds0
H-bond Acceptor0
H-bond Donor0
Chemical Classificationhalogenated compounds
CHEBI-ID39282

mVOC Specific Details

Boiling Point
DegreeReference
42.5 °C peer reviewed
Volatilization
The Henry's Law constant for methyl iodide is 0.00526 atm-cu m/mole at 25 deg C(1). This Henry's Law constant indicates that methyl iodide should volatilize from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 1.3 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 4.8 days(SRC). The Henry's Law constant in seawater of salinity 30.4 g dissolved inorganic matter/kg seawater was 0.00354 atm-cu m/mole at 20 deg C(4) indicating a lower volatization rate for methyl iodide in seawater(SRC). Dissipation of methyl iodide from open surface water was found to be primarily a result of volatilization(4). Experiments conducted under indoor conditions resulted in a first-order half-life of 29 hours under static conditions and 6.5 hours when stirred at low speed with a magnetic stirrer(5). After 6 days, less that 1% of the methyl iodide was detected as iodide ion. Methyl iodide's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). Methyl iodide is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 405 mm Hg at 25 deg C(3).
Literature: (1) Hunter-Smith RJ et al; Tellus Ser B B35: 170-6 (1983) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Boublik T et al; The Vapor Pressures of Pure Substances Amsterdam: Elsevier p. 51 (1984) (4) Moore RM et al; Chemosphere 30: 183- 91 (1995) (5) Gan J, Yates SR; J Agric Food Chem 44: 4001-8 (1996)
Literature: #Experiments were conducted to assess the volatilization loss of methyl iodide, applied at 30 cm, from 60-cm packed soil columns with different soils and under various soil surface conditions(1). In Greenfield sandy loam, the greatest cumulative loss occurred in nontarp applications, 94%, and the least in a high-barrier plastic tarp treatment, 75%. Volatilization losses with a polyethylene film was 90% and therefore this treatment was ineffective at preventing volatilization loss. Volatilization losses using a polyethylene film were significantly lower, 38% and 53%, from two soils high in organic matter and capable of rapidly degrading the chemical.
Literature: (1) Gan J et al; J Environ Qual 26: 1107-15 (1997)
Soil Adsorption
Using a structure estimation method based on molecular connectivity indices(1), the Koc for methyl iodide can be estimated to be 14(SRC). According to a classification scheme(2), this estimated Koc value suggests that methyl iodide should have very high mobility in soil. The soil/water distribution coefficient of methyl iodide in various soils were (soil, Kd): Greenfield sandy loam, 0.09; Linne clay loam, 0.15; Carsetas loamy sand, 0.16; and potting mix, 0.55(3).
Literature: (1) Meylan WM et al; Environ Sci Technol 26: 1560-67 (1992) (2) Swann RL et al; Res Rev 85: 17-28 (1983) (3) Gan J, Yates SR; J Agric Food Chem 44: 4001-8 (1996) (4) Gan J et al; J Environ Qual 26: 1107-15 (1997)
Vapor Pressure
PressureReference
4.05X10+2 mm Hg @ 25 deg CBoublik, T., Fried, V., and Hala, E., The Vapour Pressures of Pure Substances. Second Revised Edition. Amsterdam: Elsevier, 1984., p. 51
Massbank-Links

Species emitting the compound
KingdomSpeciesBiological FunctionOrigin/HabitatReference
ProkaryotaRhizobium Sp.n/aNASchulz and Dickschat 2007
ProkaryotaSphingomonas Sp.n/aNASchulz and Dickschat 2007
ProkaryotaVariovorax Sp.n/aNASchulz and Dickschat 2007
ProkaryotaPseudomonas Sp.n/aNASchulz and Dickschat 2007
ProkaryotaRhodococcus Sp.n/aNASchulz and Dickschat 2007
ProkaryotaRoseovarius Sp.n/aNASchulz and Dickschat 2007
ProkaryotaMethanobacterium Sp.n/aNASchulz and Dickschat 2007
ProkaryotaZoogloea Sp.n/aNASchulz and Dickschat 2007
ProkaryotaAlteromonas Sp.n/aNASchulz and Dickschat 2007
ProkaryotaDeleya Sp.n/aNASchulz and Dickschat 2007
ProkaryotaPhotobacterium Sp.n/aNASchulz and Dickschat 2007
ProkaryotaPseudoalteromonas Sp.n/aNASchulz and Dickschat 2007
ProkaryotaShewanella Sp.n/aNASchulz and Dickschat 2007
ProkaryotaVibrio Sp.n/aNASchulz and Dickschat 2007
ProkaryotaMyxobacterium Sp.n/aNASchulz and Dickschat 2007
ProkaryotaPlantibacter Sp.n/aNASchulz and Dickschat 2007
Method
KingdomSpeciesGrowth MediumApplied MethodVerification
ProkaryotaRhizobium Sp.n/an/ano
ProkaryotaSphingomonas Sp.n/an/ano
ProkaryotaVariovorax Sp.n/an/ano
ProkaryotaPseudomonas Sp.n/an/ano
ProkaryotaRhodococcus Sp.n/an/ano
ProkaryotaRoseovarius Sp.n/an/ano
ProkaryotaMethanobacterium Sp.n/an/ano
ProkaryotaZoogloea Sp.n/an/ano
ProkaryotaAlteromonas Sp.n/an/ano
ProkaryotaDeleya Sp.n/an/ano
ProkaryotaPhotobacterium Sp.n/an/ano
ProkaryotaPseudoalteromonas Sp.n/an/ano
ProkaryotaShewanella Sp.n/an/ano
ProkaryotaVibrio Sp.n/an/ano
ProkaryotaMyxobacterium Sp.n/an/ano
ProkaryotaPlantibacter Sp.n/an/ano