indole

1H-Indole

120-72-9

2,3-Benzopyrrole

Indol

1-Benzazole

Ketole

1-Azaindene

Benzopyrrole

2,3-Benzopyrole

Indole (natural)

Caswell No. 498B

1-Benzo(b)pyrrole

Indol [German]

FEMA No. 2593

CCRIS 4421

HSDB 599

EPA Pesticide Chemical Code 025000

1H-Benzo[b]pyrrole

Benzo[b]pyrrole

AI3-01540

NSC 1964

EINECS 204-420-7

MFCD00005607

UNII-8724FJW4M5

INDOLUM

DTXSID0020737

CHEBI:16881

8724FJW4M5

NSC-1964

CHEMBL15844

DTXCID40737

Indole 100 microg/mL in Acetonitrile

NCGC00167539-01

INDOLE (USP-RS)

INDOLE [USP-RS]

IND

CAS-120-72-9

benzazole

mono-indole

1-H-indole

Indole, 7

Indole (8CI)

Indole (white flake)

Indole, 98%

1H-Indole (9CI)

INDOLUM [HPUS]

INDOLE [FHFI]

INDOLE [HSDB]

INDOLE [FCC]

INDOLE [MI]

Indole, >=99%

SCHEMBL698

bmse000097

Indole, analytical standard

Indole, >=99%, FG

WLN: T56 BMJ

BIDD:GT0304

SCHEMBL940818

INDOLE BENZO-PYRROLE

SCHEMBL1921769

SCHEMBL9559244

AMY3411

NSC1964

185l

BCP27232

STR01201

Tox21_112536

Tox21_201677

Tox21_302937

BBL011739

BDBM50094702

s6358

STL163380

Indole, 3-Benzopyrrole, 1-benzazole

AKOS000119629

Tox21_112536_1

AT36838

CG-0501

CS-W001132

DB04532

HY-W001132

Indole, puriss., >=98.5% (GC)

MCULE-9442796928

NCGC00167539-02

NCGC00167539-03

NCGC00256348-01

NCGC00259226-01

BP-10563

DS-011308

I0021

NS00010849

EN300-18285

C00463

I-0800

I-0810

Q319541

SR-01000944736

SR-01000944736-1

Z57833933

F2190-0647

InChI=1/C8H7N/c1-2-4-8-7(3-1)5-6-9-8/h1-6,9

82451-55-6

The Henry's Law constant for indole is estimated as 5.3X10-7 atm-cu m/mole(SRC) from its experimental values for vapor pressure, 0.0122 mm Hg(1), and water solubility, 3560 mg/l(2). This value indicates that indole will be essentially nonvolatile from water surfaces(3,SRC). Indole's Henry's Law constant(1,2,SRC) indicates that volatilization from moist soil surfaces should not occur(SRC).
Literature: (1) Yaws CL; Handbook of Vapor Pressure. Volume 3. C8 to C28 Compounds. HOuston,TX: Gulf Publ Co (1994) (2) Yalkowsky SH, Dannenfelser RM; Aquasol Database of Aqueous Solubility. Ver 5. College of Pharmacy, University of Arizona - Tucson, AZ. PC Ver (1992) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington DC: Amer Chem Soc pp. 15-1 to 15-29 (1990)

A Koc of 187 was measured for indole on a synthetic soil consisting of 88-90% sand, 10% clay and 0-2% humic acid(1). The Koc of indole is estimated as approximately 350(SRC), using a measured log Kow of 2.14(2) and a regression-derived equation(3,SRC). According to a recommended classification scheme(4), these Koc values suggest that indole has moderate mobility in soil(SRC).
Literature: (1) Rebhun M et al; Water Res 26: 79-84 (1992) (2) Hansch C et al; Exploring QSAR. Hydrophobic, Electronic, and Steric Constants. ACS Prof Ref Book. Amer Chem Soc, Washington, DC. p. 6 (1995) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington DC: Amer Chem Soc pp. 4-9 (1990) (4) Swann RL et al; Res Rev 85: 23 (1983)

TETRANITROMETHANE

509-14-8

Methane, tetranitro-

RCRA waste number P112

NCI-C55947

Tetranitromethane(Technical)

K1G7CKU98F

TNM

DTXSID5021334

CHEBI:82372

Tetan

NSC-16146

DTXCID201334

NSC 16146

CAS-509-14-8

CCRIS 2371

HSDB 852

EINECS 208-094-7

UN1510

RCRA waste no. P112

UNII-K1G7CKU98F

WLN: WNXNWNWNW

SCHEMBL71873

TETRANITROMETHANE [MI]

CHEMBL261663

TETRANITROMETHANE [HSDB]

TETRANITROMETHANE [IARC]

NSC16146

Tox21_202353

Tox21_302834

UN 1510

NCGC00091783-01

NCGC00091783-02

NCGC00091783-03

NCGC00256516-01

NCGC00259902-01

Tetranitromethane [UN1510] [Oxidizer]

DB-051865

NS00022261

C19300

Q412241

The Henry's Law constant for tetranitromethane is estimated as 0.0024 atm-cu m/mole(SRC) derived from its vapor pressure, 8.42 mm Hg(1), and water solubility, 900 mg/L(2). This Henry's Law constant indicates that tetranitromethane is expected to volatilize rapidly from water surfaces(3). 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)(3) is estimated as 2 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)(3) is estimated as 6 days(SRC). Tetranitromethane estimated Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of tetranitromethane from dry soil surfaces may exist(SRC) based upon its vapor pressure(1).

The Koc of tetranitromethane is estimated as 100(SRC), using a water solubility of 900 mg/L(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that tetranitromethane is expected to have high mobility in soil(SRC).

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)

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)