METHYL BENZOATE

93-58-3

Methylbenzoate

Benzoic acid, methyl ester

benzoic acid methyl ester

Clorius

Methyl benzenecarboxylate

Essence of niobe

Oxidate le

FEMA No. 2683

Methyl benzoate (natural)

Methylester kyseliny benzoove

NSC 9394

CCRIS 5851

HSDB 5283

EINECS 202-259-7

UNII-6618K1VJ9T

DTXSID5025572

CHEBI:72775

AI3-00525

CLORIUS-

6618K1VJ9T

NSC-9394

MFCD00008421

Methyl ester of benzoic acid

DTXCID405572

EC 202-259-7

CAS-93-58-3

UN2938

Methylester kyseliny benzoove [Czech]

Benzoato de metilo

methyloxycarbonylbenzene

benzoic acid methylester

Methyl benzoate, 99%

Methyl-benzenecarboxylate

Benzoic acid-methyl ester

WLN: 1OVR

SCHEMBL7200

METHYL BENZOATE [MI]

MLS001050185

CHEMBL16435

METHYL BENZOATE [FCC]

METHYL BENZOATE [FHFI]

METHYL BENZOATE [HSDB]

METHYL BENZOATE [INCI]

SCHEMBL4790973

SCHEMBL10330498

NSC9394

Methyl benzoate, >=99% (GC)

Methyl benzoate, analytical standard

Tox21_201832

Tox21_303198

BBL010502

STK021498

AKOS000120640

Methyl benzoate, >=98%, FCC, FG

AT34734

MCULE-3681534655

UN 2938

Methyl benzoate, for synthesis, 98.0%

NCGC00091665-01

NCGC00091665-02

NCGC00256939-01

NCGC00259381-01

BP-31073

SMR001216584

VS-02533

B0074

NS00012849

EN300-15500

Methyl benzoate, natural, >=98%, FCC, FG

C20645

A844641

Q417328

J-522592

Methyl benzoate [UN2938] [Keep away from food]

Z19825577

F0001-2239

InChI=1/C8H8O2/c1-10-8(9)7-5-3-2-4-6-7/h2-6H,1H

The Henry's Law constant for methyl benzoate is estimated as 3.24X10-5 atm-cu m/mole(SRC) derived from its vapor pressure, 0.38 mm Hg(1), and water solubility, 2.1X10+3 mg/L(2). This Henry's Law constant indicates that methyl benzoate is expected to volatilize 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 22 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 14 days(SRC). Methyl benzoate's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). Methyl benzoate is not expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 0.38 mm Hg(1).
Literature: (1) Daubert TE, Danner RP; Data Compilation Tables of Properties of Pure Compounds New York, NY: Amer Inst for Phys Prop Data (1989) (2) Riddick JA et al; Organic Solvents 4th ed. New York, NY: Wiley (1986) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990)

The adsorption of methyl benzoate was determined by a modified version of the OECD guideline 106, a batch equilibrium method, in three soils with different characteristics: an acid forest soil (Podzol), an agricultural soil (Alfisol), and a sediment. The respective Freundlich constants, Kf (1/n), for the three soils were 8.64 (0.81), 1.29 (0.85), and 1.51 (0.84)(1). Koc values for the Podzol, Alfisol and sediment were 178, 103, and 95, respectively(1). Methyl benzoate also has a reported log Koc value of 2.10 (Koc = 126)(2). Using a structure estimation method based on molecular connectivity indices(3), the Koc of methyl benzoate can be estimated to be 70(SRC). According to a classification scheme(3), methyl benzoate is expected to have moderate to high mobility in soil.
Literature: (1) Von Oepen B et al; Chemosphere 22: 285-304 (1991) (2) Schuurmann G et al; Environ Sci Technol 40: 7005-11 (2006) (3) Swann RL et al; Res Rev 85: 17-28 (1983)

dimethyl sulfide

Methyl sulfide

75-18-3

Methane, thiobis-

dimethyl sulphide

dimethylsulfide

Methyl thioether

Dimethylsulphide

2-Thiapropane

Dimethyl thioether

Methyl sulphide

METHYLSULFANYLMETHANE

Methylthiomethane

Dimethylsulfid

(Methylsulfanyl)methane

Methyl monosulfide

Dimethyl monosulfide

Thiobismethane

2-Thiopropane

Methanethiomethane

Thiobis(methane)

Exact-S

Sulfure de methyle

Dimethyl sulfide (natural)

dimethylsulfane

FEMA No. 2746

Methylthiomethyl radical

MFCD00008562

Methane, 1,1'-thiobis-

[SMe2]

QS3J7O7L3U

CHEBI:17437

(CH3)2S

31533-72-9

methylsulfide

Dimethylsulfid [Czech]

Sulfure de methyle [French]

HSDB 356

EINECS 200-846-2

UN1164

UNII-QS3J7O7L3U

BRN 1696847

Methylsulphide

Thiopropane

Thiobis-methane

di-methylsulfide

AI3-25274

Dimethyl sulfane

Sulfide, methyl-

(methylthio)methane

Me2S

REDUCED-DMSO

SMe2

Dimethyl sulfide, 98%

reduced dimethyl sulfoxide

(Methylsulfanyl)methane #

Dimethyl sulfide [UN1164] [Flammable liquid]

Dimethyl sulfoxide(Reduced)

EC 200-846-2

(Me)2S

Dimethyl sulfide, >=99%

4-01-00-01275 (Beilstein Handbook Reference)

CHEMBL15580

DIMETHYL SULFIDE [MI]

METHYL SULFIDE [FHFI]

DIMETHYL SULFIDE [FCC]

DIMETHYL SULFIDE [HSDB]

DTXSID9026398

S(CH3)2

Dimethyl sulfide, >=99%, FCC

Dimethyl sulfide, analytical standard

STL481894

Dimethyl sulfide, >=95.0% (GC)

AKOS009031411

MCULE-4525381422

UN 1164

Dimethyl sulfide, anhydrous, >=99.0%

InChI=1/C2H6S/c1-3-2/h1-2H

M0431

NS00005000

NS00124710

Dimethyl sulfide, puriss., >=99.0% (GC)

C00580

Dimethyl sulfide, natural, >=99%, FCC, FG

Dimethyl sulfide [UN1164] [Flammable liquid]

A838342

Dimethyl sulfide, redistilled, >=99%, FCC, FG

Q423133

Q-100810

The Henry's Law constant for dimethyl sulfide has been measured as 1.61X10-3 atm-cu m/mole(1). This Henry's Law constant indicates that dimethyl sulfide 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 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 3 days(SRC). Dimethyl sulfides's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of dimethyl sulfide from dry soil surfaces may exist(SRC) based upon a vapor pressure of 502 mm Hg(3).
Literature: (1) Gaffney, JS et al; Env Sci Tech 21: 519-23 (1987) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals: Data Compilation. Vol 4. Design Inst Phys Prop Data, Amer Inst Chem Eng, NY, NY: Hemisphere Pub Corp (1989)

The Koc of dimethyl sulfide is estimated as 6.3(SRC), using a water solubility of 22,000 mg/L(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that dimethyl sulfide is expected to have very high mobility in soil.
Literature: (1) Suzuki T; J Comp-Aided Molec Des 5: 149-66 (1991) (2) US EPA; Estimation Program Interface (EPI) Suite. Ver. 4.0. Jan, 2009. Available from http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm as of Oct 1, 2009. (3) Swann RL et al; Res Rev 85: 17-28 (1983)
Literature: #Air-dried, unsterilized moist, and sterilized moist soils exposed to air initially containing 500 ppm dimethyl sulfide adsorbed an avg of 32, 308, and 10 ug dimethyl sulfide/g soil, respectively, in 15 days(1). Time required for complete sorption of dimethyl sulfide by moist soil from air initially containing 100 ppm dimethyl sulfide: soil 1 (Weller) - 1st exposure 150 min, 2nd exposure 100 min, 3rd exposure 95 min; soil 2 (Harps) - 1st exposure 45 min, 2nd exposure 24 min, 3rd exposure 19 min(1). These data suggest that moist soils have a greater tendency to adsorb dimethyl sulfide than dry soils, and that microbial activity in moist soils may be responsible for greater adsorption(1). When natural gas containing 0.5 pounds of dimethyl sulfide per million cubic feet of gas was passed through a bed of pulverized, dry, montmorillonite clay, dimethyl sulfide exhibited a fast breakthrough (2 hours) and a fast build-up rate in effluent gas (85% of influent concn 4 hours after breakthrough), suggesting that dimethyl sulfide does not adsorb to dry soils(2).
Literature: (1) Bremner JM, Banwart WL; Soil Biol Biochem 8: 79-83 (1976) (2) Williams RP; Oper Sect Proc - Am Gas Assoc pp. T29-T37 (1976)