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)

methyleneiodide

methvleneiodide

DIIODOMETHANE

Diidomethane

Methylenjodid

Dijodmethan

QMABlZqIh@

NZZFYRREKKOMAT-UHFFFAOYSA-N

Methylene diiodide

Methylene iodide

Methyl diiodide

diiodo-methane

bis(iodanyl)methane

AC1L1MBR

Diiodomethane, stabilized with Copper chip

Di-iodomethane; Methylene iodide

MI-Gee

ACMC-1BGAZ

CH2I2

Methylenjodid [Czech]

Mi-gee brand

SCHEMBL185

Dijodmethan [Czech]

K284

KSC377G1H

Methane, diiodo-

METHYL, DIIODO-

KM1670

WLN: I1I

D0610

CTK2H7313

NSC35804

STR03006

CCRIS 8551

OR228626

FS000809

OR020175

DTXSID4058784

BBL011419

STL146526

AK121968

A838327

AN-23838

SC-16458

3J731705OX

NSC 35804

NSC-35804

ANW-13590

BP-21047

ST2406799

LS-90036

KB-76592

BB_SC-6852

MFCD00001079

TR-024206

UNII-3J731705OX

RTR-024206

AKOS002664705

I14-0204

FT-0628875

75-11-6

F0001-1891

Diiodomethane, 99%, stabilized 25g

Diiodomethane, SAJ first grade, >=98.0%

MCULE-8023612181

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

EINECS 200-841-5

103883-81-4

MolPort-000-150-264

Triiodomethane

Trijodmethane

OKJPEAGHQZHRQV-UHFFFAOYSA-N

Jodoform

IODOFORM

Carbon triiodide

Dezinfekt V

tris(iodanyl)methane

AC1L1MDX

CHI3

Trijodmethane [Czech]

WLN: IYII

Methane, triiodo-

Iodoform, SAJ first grade

KSC377O0R

Jodoform [Czech]

K290

ACMC-20akq1

Iodoform [JAN]

Iodoform (TN)

CTK2H7708

Iodoform, 99%

CCRIS 346

NSC26251

CM10958

EBD19519

HSDB 4099

KXI2J76489

D01910

C13383

DSSTox_CID_743

LTBB002749

OR337763

LS-1666

CHEMBL1451116

DTXSID4020743

OR020244

OR271428

NCI-C04568

UNII-KXI2J76489

ZINC6827595

A838427

CHEBI:37758

AN-23858

TRA0080382

SC-16447

AB1001960

DSSTox_GSID_20743

NSC-26251

NSC 26251

Iodoform (JP17/USP)

MFCD00001069

DSSTox_RID_75765

AI3-52396

TR-024271

RTR-024271

I14-7271

J-650249

AKOS009031506

FT-0627266

75-47-8

Iodoform, 99% 50g

Tox21_111124

Tox21_202389

Tox21_302774

METHYL, TRIIODO-(8CI,9CI)

CAS-75-47-8

NCGC00259938-01

MCULE-5976787287

NCGC00091389-01

NCGC00091389-02

NCGC00091389-03

NCGC00256394-01

EINECS 200-874-5

MolPort-001-783-761

Iodoform, purum, >=99.0% (AT)

Iodoform, puriss., 99.0-100.5%

The Henry's Law constant for iodoform is estimated as 3.1 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that iodoform is expected to 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 40 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 25 days(SRC). Iodoform's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). Iodoform is not expected to volatilize from dry soil surfaces(SRC) based upon an estimated vapor pressure of 0.040 mm Hg(SRC), determined from a fragment constant method(3).
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) Lyman WJ; p 31 in Environmental Exposure From Chemicals Vol I, Neely WB, Blau GE(eds), Boca Raton, FL: CRC Press (1985)

Using a structure estimation method based on molecular connectivity indices(1), the Koc for iodoform can be estimated to be 35(SRC). According to a classification scheme(2), this estimated Koc value suggests that iodoform is expected to have very high 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)

CHLOROIODOMETHANE

iodochloromethane

Methylene chloroiodide

QMABlXaIh@

Chloromethyl iodide

PJGJQVRXEUVAFT-UHFFFAOYSA-

PJGJQVRXEUVAFT-UHFFFAOYSA-N

chloro-iodomethane

chloroiodo-methane

chloranyl(iodanyl)methane

CH2ClI

Chloro-iodo-methane

chloro(iodo)methane

AC1Q3VDA

chlor(iod)methan

Chloroiodomethane, 97%

AC1L1XT0

Methane, chloroiodo-

Chloroiodomethane, stab. with copper

KSC275C3N

O680

SCHEMBL35847

ACMC-209mct

c1179

CTK1H5136

OR30688

RP23810

OR022020

M-2678

A832287

KB-48864

ANW-33243

AN-46233

BP-10639

SC-22871

DTXSID50208034

AB0016593

TRA0169562

MFCD00001078

3S109956

DB-053375

TR-020602

RTR-020602

S14-0715

AKOS015850790

Chloroiodomethane, 98%, stabilized 10g

593-71-5

EINECS 209-804-8

MolPort-001-783-988

InChI=1/CH2ClI/c2-1-3/h1H2