acetylmethylcarbinol

Dimethylketol

Acethoin

acetoine

ROWKJAVDOGWPAT-UHFFFAOYSA-N

acetoin

NATURAL ACETOIN

Acetyl methyl carbinol

acetylmethyl-

beta-oxobutane

Methanol, acetylmethyl

3-Hydroxybutanone

b-oxobutane

Acetoin, analytical standard

DL-Acetoin

gamma-Hydroxy-beta-oxobutane

1-Hydroxyethyl methyl ketone

Methanol, acetylmethyl-

1-Hydroxethyl methyl ketone

2-Acetoin

Acetyl Methyl Carbinol, Natural

AC1L18NL

AC1Q1JA8

Acetoin (natural)

KSC490C7N

2,3-Butanolone

3-Hydroxy-2-butanone; Acetylmethylcarbinol

NSC7609

UN2621

2-hydroxy-3-oxobutane

3-hydroxy-2-oxobutane

3-hydroxyl-2-butanone

Acetoin, May exist as crystalline dimer

CTK3J0176

HMDB03243

HSDB 974

2-Hydroxy-3-butanone

3-hydroxy-2-butanone

3-hydroxy-2-butanone, hydroxybutanone

3-hydroxybutan-2-one

LS-164

NSC89727

RP18489

C00466

CCRIS 2918

LTBB004792

2-Butanol-3-one

3-Oxo-2-butanol

AK128843

CHEMBL3561873

DTXSID0024399

NSC 7609

NSC-7609

OR035239

OR108639

OR315616

UN 2621

Acetoin, >=96%, natural

CHEBI:15688

DSSTox_CID_4399

2-butanone, 3-hydroxy

3-hydroxy-butan-2-one

AB1002764

AN-45468

ANW-31250

DSSTox_GSID_24399

KB-32104

NSC-89727

SC-18553

DSSTox_RID_77389

LMFA12000020

MFCD00004521

MFCD00038696

AI3-03314

Butan-2-ol-3-one

DB-003392

RTR-018308

ST24042214

TR-018308

.gamma.-Hydroxy-.beta.-oxobutane

AKOS000121293

AKOS017278202

I09-0138

Q-200581

2-Butanone, 3-hydroxy-

BRN 0385636

FEMA No. 2008

FT-0621797

FT-0695713

Acetoin, natural, >=95%, FG

Tox21_302518

513-86-0

F0001-1338

PROPOXY, 1-METHYL-2-OXO-

(+/-)-Acetoin

Acetoin, >=96%, FCC, FG

Butan-2-one, 3-hydroxy-

MCULE-5374414264

NCGC00256914-01

CAS-513-86-0

EINECS 208-174-1

51555-24-9

52217-02-4

Acetyl methyl carbinol [UN2621] [Flammable liquid]

MolPort-001-785-644

Acetyl methyl carbinol [UN2621] [Flammable liquid]

(+/-)-3-Hydroxybutan-2-one

2-Butanone, 3-hydroxy- (8CI,9CI)

2-Butanone, 3-hydroxy-, (R)-

2-01-00-00870 (Beilstein Handbook Reference)

2-Butanone, 3-hydroxy-, (.+/-.)-

The Henry's Law constant for acetoin is estimated as 1.0X0-5 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that acetoin 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 2 days(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 28 days(SRC). Acetoin's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). Acetoin is expected to volatilize from dry soil surfaces(SRC) based upon an estimated vapor pressure of 2.7 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)

The Koc of acetoin is estimated as 2(SRC), using a water solubility of 1.0X10+6 mg/L(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that aetoin is expected to have very high mobility in soil.
Literature: (1) Yalkowsky SH, Dannenfelser RM; The AQUASOL DATABASE of Aqueous Solubility. Ver 5. Tucson, AZ: Univ AZ, College of Pharmacy (1992) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-5 (1990) (3) Swann RL et al; Res Rev 85: 17-28 (1983)

METHYLSULFANYLMETHANE

Methanethiomethane

Dimethylsulphide

Methylthiomethane

dimethylsulfane

Dimethylsulfid

dimethylsulfide

Methylsulphide

Methylthiomethyl radical

Thiobismethane

(Methylthiomethylidyne)radical

methylsulfide

Dimethyl monosulfide

Thiopropane

dimethyl sulphide

Dimethyl thioether

Methyl monosulfide

QMMFVYPAHWMCMS-UHFFFAOYSA-N

reduced dimethyl sulfoxide

dimethyl sulfide

Methyl sulphide

Methyl thioether

Thiobis-methane

(Methylsulfanyl)methane

Methyl sulfide

REDUCED-DMSO

(methylthio)methane

Dimethyl sulfide, analytical standard

Dimethyl sulfoxide(Reduced)

Sulfure de methyle

(Methylsulfanyl)methane #

2-Thiapropane

2-Thiopropane

AC1L1ANN

Exact-S

Thiobis(methane)

ACMC-1BBLH

C2H6S

Dimethylsulfid [Czech]

Nat. Dimethyl Sulfide

Dimethyl sulfide (natural)

Methane, thiobis-

QS3J7O7L3U

KSC377G0P

Sulfide, methyl-

6873AF

CHEMBL15580

Dimethyl sulfide, >=99%

UN1164

UNII-QS3J7O7L3U

CTK2H7307

Dimethyl sulfide, 98%

HMDB02303

HSDB 356

M0431

[SMe2]

RP18263

Sulfure de methyle [French]

C00580

LTBB002388

(CH3)2S

DTXSID9026398

LS-2960

methyl sulphide, dimethyl sulphide, exact-S, thiobismethane

OR000121

OR337379

STL481894

UN 1164

A838342

CHEBI:17437

AN-23841

ANW-36574

KB-76628

SC-26847

Dimethyl sulfide, >=99%, FCC

MFCD00008562

AI3-25274

RTR-024212

TR-024212

AKOS009031411

I09-0087

Q-100810

BRN 1696847

Dimethyl sulfide, anhydrous, >=99.0%

FEMA No. 2746

FT-0603084

Methane, 1,1'-thiobis-

75-18-3

Dimethyl sulfide, 99% 250ml

MCULE-4525381422

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

EINECS 200-846-2

31533-72-9

Dimethyl sulfide [UN1164] [Flammable liquid]

Dimethyl sulfide, >=95.0% (GC)

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

MolPort-003-928-951

Dimethyl sulfide [UN1164] [Flammable liquid]

13741-EP2269977A2

13741-EP2277865A1

13741-EP2280006A1

13741-EP2284171A1

13741-EP2287153A1

13741-EP2298767A1

13741-EP2305656A1

13741-EP2308851A1

13741-EP2308873A1

13741-EP2311820A1

13741-EP2314576A1

13741-EP2314587A1

13741-EP2316836A1

13838-EP2292595A1

13838-EP2295409A1

13838-EP2295426A1

13838-EP2295427A1

13838-EP2295437A1

13838-EP2298775A1

13838-EP2311820A1

13838-EP2316836A1

18767-EP2270003A1

18767-EP2272832A1

18767-EP2277848A1

18767-EP2292576A2

18767-EP2292597A1

18767-EP2301933A1

18767-EP2305672A1

18767-EP2308510A1

18767-EP2308838A1

18767-EP2308877A1

18767-EP2311827A1

18767-EP2314576A1

18767-EP2314587A1

47704-EP2280006A1

47704-EP2311811A1

80926-EP2295426A1

80926-EP2295427A1

80926-EP2305687A1

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

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

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

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)

Methylnonylketone

UNDECANONE

KYWIYKKSMDLRDC-UHFFFAOYSA-N

Rue ketone

Nonyl methyl ketone

Methyl nonyl ketone

2-Hendecanone

2-Oxoundecane

2-Undecanone

AC1L1QEM

2-undecanon

Methyl Nonyl Ketone FCC

YV5DSO8CY9

METHYL N-NONYL KETONE

Ketone, methyl nonyl

AC1Q5H8X

UNII-YV5DSO8CY9

Undecan-2-one

KSC176M2T

L352

MGK Dog and Cat Repellent

ACMC-1C77Q

Mgk dog & cat repellent

NSC4028

U0006

CTK0H6629

DB08688

SCHEMBL117635

SCHEMBL249443

Undecanone-(2)

C01875

HSDB 7431

WLN: 9V1

2-Undecanone (natural)

SBB060389

AN-1415

NSC-4028

NSC 4028

STL146552

LS-3143

LP003930

Jsp000923

BBL011441

CHEMBL1236582

DTXSID2021943

ZINC1529305

CHEBI:17700

DSSTox_CID_1943

A802493

DSSTox_GSID_21943

ANW-16393

Caswell No. 573O

2-Undecanone, 99%

LMFA12000002

BB_SC-6944

MFCD00009583

DSSTox_RID_76418

AI3-03081

TR-002375

ST51046579

RTR-002375

Q-201393

EPA Pesticide Chemical Code 044102

Methyl nonyl ketone (MNK) Nonyl methyl ketone Methyldecananone 2-Hendecanone Undecanone IBI-246

BB_SC-06944

AKOS005720838

FEMA No. 3093

FT-0613466

BRN 1749573

I14-10598

2-Undecanone, natural, FCC, FG

Tox21_301385

112-12-9

MCULE-6858373499

NCGC00255160-01

NCGC00164003-01

CAS-112-12-9

EINECS 203-937-5

53452-70-3

2-Undecanone, >=98%, FCC, FG

MolPort-003-933-723

The Henry's Law constant for 2-undecanone is 6.36X10-5 atm-cu m/mole(1). This Henry's Law constant indicates that 2-undecanone 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 13 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 11 days(SRC). 2-Undecanone's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). 2-Undecanone is not expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 4.1X10-2 mm Hg(3).
Literature: (1) Buttery RG et al: J Agric Food Chem 17:385-9 (1960) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Perry RH, Green D; Perry's Chemical Handbook. Physical and Chemical data. NY,NY: McGraw-Hill 6th ed (1984)

Insoluble in water. Soluble in ethanol, ether, acetone, benzene, carbon tetrachloride, chloroform.
Literature: Lide, D.R., G.W.A. Milne (eds.). Handbook of Data on Organic Compounds. Volume I. 3rd ed. CRC Press, Inc. Boca Raton ,FL. 1994., p. V5: 5176
Literature: #In water, 20 mg/L at 25 deg C (est)
Literature: US EPA; Estimation Program Interface (EPI) Suite. Ver.3.12. Nov 30, 2004. Available from, as of Mar 3, 2006: http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm

Using a structure estimation method based on molecular connectivity indices(1), the Koc of 2-undecanone can be estimated to be 278(SRC). According to a classification scheme(2), this estimated Koc value suggests that 2-undecanone is expected to have moderate 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)

Methyldisulfanylmethane

Methyldithiomethane

dimethyldisulphide

Dimethyldisulfide

methyldisulfanyl methane

Methyldisulfide

Dimethyl disulphide

WQOXQRCZOLPYPM-UHFFFAOYSA-N

Dimethyl disulfide

methyl disulphide

Disulfide dimethyl

METHYL DISULFIDE

(Methyldisulfanyl)methane

DMDS

Sulfa-hitech

Dimethyl disulfide, analytical standard

(Methyldithio)methane

(Methyldisulfanyl)methane #

Disulfide, dimethyl

AC1Q4HER

AC1Q4HEQ

1,2-Dimethyldisulfane

PubChem9665

Dimethyl disulfide, >=99%

AC1L1Z53

2,3-Dithiabutane

Dimethyl disulfide, 99%

NSC9370

UN2381

Dimethyl disulfide, 98%

HMDB05879

D0714

CTK2F3131

RP18575

CHEBI:4608

CCRIS 2939

C08371

BDBM233038

Methyl disulfide (8CI)

WLN: 1SS1

3P8D642K5E

HSDB 6400

LS-1499

DTXSID4025117

NSC 9370

NSC-9370

OR000230

OR291634

CHEMBL1347061

Sulfa-hitech 0382

UN 2381

(1/4)x>>u paragraph signthornAoAN

(CH3S)2

UNII-3P8D642K5E

ZINC8221057

A833808

Dimethyl disulfide, >=99.0%

DSSTox_CID_5117

KB-76616

AN-22028

TL8004165

Dimethyl disulfide, >=98%, FG

DSSTox_GSID_25117

DSSTox_RID_77673

MFCD00008561

AI3-25305

TR-021489

RTR-021489

I09-0129

Q-100719

AKOS009157459

FEMA No. 3536

FT-0625135

METHYL, [(THIOMETHYL)THIO]-

Dimethyl disulfide, natural, >=98%, FG

EN300-36043

Tox21_201525

F0001-1676

624-92-0

NCGC00259075-01

NCGC00091798-02

NCGC00091798-01

MCULE-7451882535

EINECS 272-923-9

CAS-624-92-0

Dimethyl disulfide [UN2381] [Flammable liquid]

EINECS 210-871-0

Dimethyl disulfide [UN2381] [Flammable liquid]

MolPort-003-929-787

Dimethyl disulfide, purum, >=98.0% (GC)

224638-EP2371831A1

InChI=1/C2H6S2/c1-3-4-2/h1-2H

The Henry's Law constant for dimethyl disulfide is reported as 1.21X10-3 atm-cu m/mole(1). This Henry's Law constant indicates that dimethyl disulfide 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 3.5 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 4.1 days(SRC). Dimethyl disulfide's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). In a laboratory study, the volatilization rate of dimethyl disulfide from a tidal marsh soil (at field capacity or 1.5 field capacity) ranged from 0.1 to 0.4 ng (sulfur basis)/min(3). Dimethyl disulfide is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 28.7 mm Hg(4).
Literature: (1) Vitenberg AG et al; J Chromatography 112: 319-27 (1975) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Farwell SO et al; Soil Biol Biochem 11: 411-5 (1979) (4) Daubert TE, Danner RP; Physical & Thermodynamic Properties of Pure Chemicals: Data Compilation. New York, NY: Hemisphere Pub Corp (1989)

Using a structure estimation method based on molecular connectivity indices(1), the Koc of dimethyl disulfide can be estimated to be 40(SRC). According to a classification scheme(2), this estimated Koc value suggests that dimethyl disulfide is expected to have very high mobility in soil. Gas chromatographic studies with various air-dry and moist soils have shown that soil can sorb atmospheric, gas phase dimethyl disulfide(3). In one closed-system test, 17-94% of input dimethyl disulfide was sorbed by the soil in 10 min(3); in a 15-day test, dimethyl disulfide sorption was 101-306 ug sorbed/g soil(3). Soil microbes were found to be important for the gas phase sorption of dimethyl disulfide as 15-day sorption in sterilized soil was only 9-98 ug sorbed/g soil(3).
Literature: (1) US EPA; Estimation Program Interface (EPI) Suite. Ver. 4.1. Jan, 2011. Available from, as of Nov 7, 2013: http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm (2) Swann RL et al; Res Rev 85: 17-28 (1983) (3) Bremner JM, Banwart WL; Soil Biol Biochem 8: 79-83 (1976)

Vinyloxyethanol

Ethyleneglycol monovinyl ester

Ethylenglycol monovinyl ester

VUIWJRYTWUGOOF-UHFFFAOYSA-N

VUIWJRYTWUGOOF-UHFFFAOYSA-

Vinyl Cellosolve

Mveeg

Ethylene glycol monovinyl ether

Vinyl Glycol

2-Vinyloxyethanol

2-ethenoxyethanol

Ethylene glycol vinyl ether

2-Hydroxyethyl vinyl ether

Ethylenglycol monovinyl ester [Russian]

AC1L20SZ

AC1Q7D7T

34CNR2NAC8

2-(Ethenyloxy)ethanol

Ethylene Glycol Monovinyl Ether, stabilized with KOH

Mveeg [Russian]

KM1767

UNII-34CNR2NAC8

2-(Vinyloxy)ethanol

CTK3J3341

E0518

HSDB 7104

Ethylene glycol monovinyl ether (stabilized with KOH)

LP109558

DTXSID4075457

OR035234

AK162410

ZINC2031158

Ethylene glycol vinyl ether, 97%

A838710

ANW-43938

AB0012473

TRA0083549

TL8006670

SC-22660

AN-22129

LS-67100

CJ-07482

KB-51565

ZINC02031158

MFCD00192151

TR-024476

ST24039805

RTR-024476

2-(ethenyloxy)ethan-1-ol

W-104362

AKOS015904282

I14-6387

FT-0651609

BRN 1739297

I14-16845

Ethanol, 2-(ethenyloxy)-

ETHANOL, 2-(VINYLOXY)-

764-48-7

Ethylene glycol vinyl ether, 97% 10ml

EINECS 212-124-4

MolPort-001-789-883

55456-EP2308865A1

55456-EP2284165A1

Ethanol, 2-(ethenyloxy)- (9CI)

InChI=1/C4H8O2/c1-2-6-4-3-5/h2,5H,1,3-4H2

The Henry's Law constant for ethylene glycol monovinyl ether is estimated as 2.5X10-7 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that ethylene glycol monovinyl ether is expected to be essentially nonvolatile from water surfaces(2). The potential for volatilization of ethylene glycol monovinyl ether from dry soil surfaces may exist(SRC) based upon an estimated vapor pressure of 2.2 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)

Soluble in ethanol, ether, and benzene
Literature: Lide, D.R. (ed.). CRC Handbook of Chemistry and Physics. 83rd ed. Boca Raton, Fl: CRC Press Inc., 2002-2003., p. 3-159

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