Iodomethylidyneradical

Monoiodomethane

iodornethane

Methyliodide

methyliodine

Methyljodide

Monoiodmethan

Iodocarbon

Iodometano

iodomethan

IODOMETHANE

Joodmethaan

Methyliodid

Methyljodid

INQOMBQAUSQDDS-UHFFFAOYSA-N

Iodmethan

RFDEYF@

Methyl iodide

Methyl iodine

Methyl-iodide

iodo methane

iodo-methane

metyl iodide

Metylu jodek

Monoioduro di metile

Jod-methan

1-iodomethane

CH3I

Iodure de methyle

meth-yl iodide

DAT010ZJSR

AC1L1MA9

AC1Q38HY

Iodometano [Italian]

Joodmethaan [Dutch]

Methyljodid [German]

Methyljodide [Dutch]

UNII-DAT010ZJSR

Methane, iodo-

NSC9366

UN2644

CCRIS 395

CTK2H8218

I0060

Metylu jodek [Polish]

Monoioduro di metile [Italian]

WLN: I1

ACT10179

CHEMBL115849

Jod-methan [German]

C18448

HSDB 1336

Iodure de methyle [French]

LTBB002606

RCRA waste number U138

BBL034228

DTXSID0024187

NSC 9366

NSC-9366

OR000922

OR228622

STL281179

UN 2644

CHEBI:39282

Halon 10001

AN-41969

ANW-56407

BP-11384

Iodomethane, 2M solution in tert-butyl methyl ether

LS-90046

SC-49382

MFCD00001073

TR-024159

AKOS009031541

I14-5819

Iodomethane, ampule of 100 mg

RCRA waste no. U138

FT-0628742

FT-0628743

74-88-4

I14-14230

Iodomethane, for synthesis, 99.0%

F2190-0170

InChI=1/CH3I/c1-2/h1H

Iodomethane, SAJ special grade, >=99.5%

Iodomethane, 99%, stabilized 50g

Iodomethane, SAJ first grade, >=93.0%

MCULE-1718786667

EINECS 200-819-5

Iodomethane, contains copper as stabilizer, ReagentPlus(R), 99%

147937-07-3

Methyl iodide [UN2644] [Poison]

METHYL, IODO-(6CI,8CI,9CI)

MolPort-000-156-457

Iodomethane, purum, >=99.0% (GC)

Iodomethane, contains copper as stabilizer, ReagentPlus(R), 99.5%

Iodomethane solution, 2.0 M in tert-butyl methyl ether, contains copper as stabilizer

Methyl iodide [UN2644] [Poison]

Iodomethane, puriss., redist., >=99.5% (GC)

Iodomethane solution, certified reference material, 2000 mug/mL in methanol: water (4:1)

Iodomethane, 2000 mug/mL in methanol: water (4:1), analytical standard

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)

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)