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)

alpha-Nonylethylene

Undecene

Hendecene

DCTOHCCUXLBQMS-UHFFFAOYSA-N

alpha-Undecylene

alpha-Undecene

AC1Q2VYM

1-Hendecene

Undecene-1

1-UNDECENE

Undecene (petroleum)

n-1-Undecene

Undec-1-ene

.alpha.-Undecene

5902AF

C11H22

ACMC-1CB71

U0025

U0052

CTK1A4960

S0341

UNII-FH2735S2NU component DCTOHCCUXLBQMS-UHFFFAOYSA-N

OR01835

NSC73983

AC1L2186

HSDB 1090

CCRIS 5720

DTXSID5061168

SBB009051

LP064094

STL453737

FR-2625

CHEBI:77444

ZINC1699445

KB-13370

CC-05049

ANW-37513

NSC-73983

NSC 73983

LMFA11000332

ZX-AT017311

MFCD00008956

1-Undecene, 97%

C-28171

LS-188198

ST51046389

TR-025719

1446756A8F

DB-056580

AKOS009156849

FT-0608327

UNII-1446756A8F

I14-19830

821-95-4

10004-001h

MCULE-8437878932

EINECS 212-483-7

EINECS 271-214-1

28761-27-5

MolPort-001-756-623

The Henry's Law constant for 1-undecene is estimated as 1.48 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that 1-undecene is expected to volatilize rapidly 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 hr(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 5 days(SRC). However, the volatilization half-life does not take into account the effects of adsorption. This is apparent from the results of two EXAMS model runs, one in which the effect of adsorption was considered, yielding an estimated half-life of 21 days in a model pond 2 m deep, and one in which the effect of adsorption was ignored, yielding an estimated half-life of 42 hrs in a model pond 2 m deep(3). 1-Undecene's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). 1-Undecene is not expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 0.493 mm Hg(4).
Literature: (1) Meylan WM, Howard PH; Environ Toxicol Chem 10: 1283-93 (1991) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) USEPA; EXAMS II Computer Simulation (1987) (4) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals: Data Compilation. Design Inst Phys Prop Data, Amer Inst Chem Eng NY, NY: Hemisphere Pub Corp 5 Vol (1989)

Sol in ether, chloroform, ligroin; insol in water
Literature: Lide, D.R. (ed.). CRC Handbook of Chemistry and Physics. 79th ed. Boca Raton, FL: CRC Press Inc., 1998-1999., p. 3-327

Using a structure estimation method based on molecular connectivity indices(1), the Koc for 1-undecene can be estimated to be about 3180(SRC). According to a classification scheme(2), this estimated Koc value suggests that 1-undecene is expected to have slight mobility in soil.
Literature: (1) Meylan WM et al; Environ Sci Technol 26: 1560-67 (1992) (2) Swann RL et al; Res Rev 85: 17-28 (1983)