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)

Dimethylacetone

diathylketon

Diethylcetone

DIETHYLKETONE

Metacetone

Methacetone

FDPIMTJIUBPUKL-UHFFFAOYSA-N

Propione

dimethyl acetone

Ethyl propionyl

Diethyl ketone

DEK

diethylcetone(french)

Ethyl ketone

ethyl ethyl ketone

3-oxopentane

AC1L1OFJ

AC1Q2ROK

AC1Q5GYE

3-pentanon

3-PENTANONE

di-ethyl ketone

Pentanone-3

Diethylcetone [French]

UNII-Y4Y2BRI5UL component FDPIMTJIUBPUKL-UHFFFAOYSA-N

1,3-Dimethylacetone

3-Pentanone, analytical standard

9SLZ98M9NK

KSC492E6L

Pentan-3-one

3-Oxylatopentane-3-ylium

7317AF

CHEMBL45315

NSC8653

UN1156

UNII-9SLZ98M9NK

CTK3J2265

P0061

ACMC-209s6p

RP18460

HSDB 5301

WLN: 2V2

BBL027755

DTXSID6021820

NSC 8653

NSC-8653

OR034165

OR128391

OR245564

STL281851

UN 1156

(C2H5)2CO

1-pentan-3-one

3-Pentanone, >=99%

A845564

CHEBI:87755

DSSTox_CID_1820

ZINC1648158

AN-24339

ANW-40799

CJ-26591

DSSTox_GSID_21820

KB-33099

SC-75292

TRA0007787

BB_SC-6948

DSSTox_RID_76347

LMFA12000001

MFCD00009320

ZINC01648158

AI3-24337

LS-101912

RTR-030127

TR-030127

AKOS000119714

I14-4162

FT-0616299

96-22-0

Z234895377

Tox21_200677

F0001-2290

BUTYL, 1-METHYL-2-OXO-

CAS-96-22-0

3-Pentanone, for HPLC, 96%

3-Pentanone, ReagentPlus(R), >=99%

MCULE-8236549739

NCGC00166068-01

NCGC00166068-02

NCGC00258231-01

EINECS 202-490-3

Diethyl ketone [UN1156] [Flammable liquid]

3-Pentanone, 99% 100ml

MolPort-001-770-065

26071-EP2314558A1

92820-EP2269986A1

92820-EP2272825A2

92820-EP2295414A1

92820-EP2305649A1

Diethyl ketone [UN1156] [Flammable liquid]

103051-EP2269986A1

103051-EP2287154A1

103051-EP2289879A1

103051-EP2298753A1

103051-EP2301918A1

3-Pentanone, ReagentPlus(R), >=99.0% (GC)

InChI=1/C5H10O/c1-3-5(6)4-2/h3-4H2,1-2H

The Henry's Law constant for diethyl ketone is 5.0X10-5 atm-cu m/mole(1). This Henry's Law constant indicates that diethyl ketone 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 19 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 8.6 days(SRC). diethyl ketone's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). Diethyl ketone is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 37.7 mm Hg(3).
Literature: (1) Sander R; Compilation of Henry's Law constants for Inorganic and Organic Species of Potential Importance in Environmental Chemistry. (ver. 3) (1999). Available at http://www.henrys-law.org as of Aug 30, 2007. (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. NY, NY: Hemisphere Pub Corp, (1989)

The Koc of diethyl ketone is estimated as 82(SRC), using a log Kow of 0.99(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that diethyl ketone is expected to have high mobility in soil.
Literature: (1) Hansch C et al; Exploring QSAR. Hydrophobic, Electronic, and Steric Constants. ACS Prof Ref Book. Heller SR, consult. ed., Washington, DC: Amer Chem Soc p. 14 (1995) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-9 (1990) (3) Swann RL et al; Res Rev 85: 17-28 (1983)

OBNCKNCVKJNDBV-UHFFFAOYSA-N

Ethyl butanoate

ETHYL BUTYRATE

Ethyl Butyrate Natural

Butyric ether

Butyric ethee

Butyric ester

Butyric acid ethyl

Ethyl butyrate, analytical standard

Ethyl n-butyrate

Ethyl n-butanoate

Butanoicacid, ethyl ester

Butanoic acid ethyl ester

AC1L1PHR

Butanoic acid ethyl estee

Butyric acid ethyl estee

Butyric acid ethyl ester

Ethyl ester of butanoic acid

AC1Q2UI5

Nat. Ethyl Butyrate

Butanoic acid, ethyl ester

SCHEMBL6115

UFD2LZ005D

n-Butyric acid ethyl ester

Butyric acid, ethyl ester

KSC489Q2R

Ethyl butyrate (natural)

NSC8857

7520AF

CHEMBL44800

UNII-UFD2LZ005D

UN1180

CTK3I9828

HSDB 406

B0759

Ethyl butyrate, 99%

NE34239

RP19237

ACMC-2098gq

LTBB002248

WLN: 3VO2

ZINC404390

CCRIS 6554

DTXSID6040111

LS-2361

UN 1180

Jsp000519

NSC 8857

NSC-8857

FEMA Number 2427

OR033993

OR197129

ZB013520

OR197602

CHEBI:88764

ANW-15240

CJ-04029

AN-17343

DSSTox_GSID_40111

SC-26823

KB-77231

DSSTox_RID_79440

MFCD00009394

DSSTox_CID_20111

LMFA07010874

ZINC00404390

RTR-001152

TR-001152

AI3-18427

J-001444

AKOS008948342

I14-2578

FT-0623347

BRN 0506331

FEMA No. 2427

TRA-0207104

Tox21_300065

F0001-0107

105-54-4

NCGC00247893-01

NCGC00253968-01

Ethyl butyrate, >=98%, FCC, FG

MCULE-9977024136

CAS-105-54-4

EINECS 203-306-4

Ethyl butyrate [UN1180] [Flammable liquid]

Ethyl butyrate, natural, >=98%, FCC, FG

MolPort-001-783-797

Ethyl butyrate [UN1180] [Flammable liquid]

4-02-00-00787 (Beilstein Handbook Reference)

InChI=1/C6H12O2/c1-3-5-6(7)8-4-2/h3-5H2,1-2H

The Henry's Law constant for ethyl n-butyrate is estimated as 4.4X10-4 atm-cu m/mole(SRC) derived from its vapor pressure, 14.0 mm Hg(1), and water solubility, 4,900 mg/L(2). This Henry's Law constant indicates that ethyl n-butyrate 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 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)(3) is estimated as 5 days(SRC). Ethyl n-butyrate's estimated Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of ethyl n-butyrate from dry soil surfaces may exist(SRC) based upon its vapor pressure(1).
Literature: (1) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Compounds Am Inst Chem Eng (1995) (2) Riddick JA et al; Organic Solvents New York, NY: John Wiley & Sons Inc. (1984) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990)

Using a structure estimation method based on molecular connectivity indices(1), the Koc of ethyl n-butyrate can be estimated to be 20(SRC). According to a classification scheme(2), this estimated Koc value suggests that ethyl n-butyrate is expected to have very high mobility in soil.
Literature: (1) US EPA; Estimation Program Interface (EPI) Suite. Ver. 4.1. Nov, 2012. Available from, as of May 13, 2015: http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm (2) Swann RL et al; Res Rev 85: 17-28 (1983)

Metylopropyloketon

Ethylacetone

Methylpropyl ketone

Pentanone

XNLICIUVMPYHGG-UHFFFAOYSA-N

Ethyl acetone

METHYL PROPYL KETONE

Methyl-propyl-cetone

Propyl methyl ketone

Metylopropyloketon [Polish]

AC1L1PSR

AC1Q2UJA

2-pentanal

2-Pentanone

Methyl Propyl Ketone FCC

pentanone-2

3bh3

Methyl n-propyl ketone

n-propyl methyl ketone

AC1Q5CH9

UNII-Y4Y2BRI5UL component XNLICIUVMPYHGG-UHFFFAOYSA-N

2-Pentanone, analytical standard

KSC176A8R

Pentan-2-on

PENTAN-2-ONE

ACMC-1C29M

CHEMBL45345

n-C3H7COCH3

NSC5350

UN1249

CTK0H6088

HSDB 158

Methyl-propyl-cetone [French]

P0060

4-methyl-2-butanone

LS-442

RP18455

2-Pentanone (natural)

C01949

LTBB001864

WLN: 3V1

ZINC901192

DTXSID0021888

FEMA Number 2842

LP124906

NSC 5350

NSC-5350

OR034164

OR133565

OR133566

OR251179

UN 1249

ZB015252

A801775

CHEBI:16472

DSSTox_CID_1888

2-Pentanone, 90%

AN-42836

ANW-15861

CJ-04530

DSSTox_GSID_21888

I97392I10V

SC-22796

TRA0046903

DSSTox_RID_76386

LMFA12000003

MFCD00009400

ZINC00901192

AI3-32118

KB-174028

RTR-001876

TR-001876

UNII-I97392I10V

AKOS000121554

I11-0032

BRN 0506058

FEMA No. 2842

FT-0613263

2-Pentanone, reagent grade, >=90%

Tox21_201670

Tox21_303016

107-87-9

F0001-0145

MCULE-7174095676

NCGC00249095-01

NCGC00256617-01

NCGC00259219-01

2-Pentanone, ultrapure grade, >=99.5%

CAS-107-87-9

EINECS 203-528-1

2-Pentanone, 99% 25g

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

2-Pentanone, ReagentPlus(R), >=99%, purified by redistillation

Methyl propyl ketone [UN1249] [Flammable liquid]

MolPort-001-783-786

2-Pentanone, for HPLC, 99.5%

92819-EP2269986A1

92819-EP2287154A1

92819-EP2289879A1

92819-EP2305649A1

161716-EP2287158A1

Methyl propyl ketone [UN1249] [Flammable liquid]

4-01-00-03271 (Beilstein Handbook Reference)

InChI=1/C5H10O/c1-3-4-5(2)6/h3-4H2,1-2H

The Henry's Law constant for 2-pentanone is 8.36X10-5 atm-cu m/mole(1). This Henry's Law constant indicates that 2-pentanone 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 12 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 6.6 days(SRC). 2-Pentanone's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). 2-Pentanone is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 35.4 mm Hg(3).
Literature: (1) Shiu WY, Mackay D; J Chem Eng Data 42: 22-30 (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) Riddick JA et al; Organic Solvents: Physical Properties and Methods of Purification 4th ed. NY, NY: Wiley Interscience (1985)

The Koc of 2-pentanone is estimated as 75(SRC), using a log Kow of 0.91(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that 2-pentanone is expected to have high mobility in soil(SRC).
Literature: (1) Hansch C et al; Exploring QSAR. Hydrophobic, Electronic, and Steric Constants. ACS Prof Ref Book. Heller SR, consult. ed., Washington, DC: Amer Chem Soc p. 14 (1995) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-9 (1990) (3) Swann RL et al; Res Rev 85: 17-28 (1983)

ZPVFWPFBNIEHGJ-UHFFFAOYSA-N

RRAHBRHPVGNOSF-UHFFFAOYSA-N

Octanone

sec-Octanone

Hexyl methyl ketone

Methyl hexyl ketone

Metyhl Hexyl Ketone

octanone-2

2-Oxooctane

2-OCTANONE

2-octanon

Methyl n-hexyl ketone

n-Hexyl methyl ketone

AC1L1Q8Z

AC1Q2VT2

AC1Q5CI1

2-Octanone, analytical standard

ACMC-1BZO5

octane-2-oxide

Octan-2-one

octan-7-one

KSC176M5B

I854

2- octanone

SCHEMBL43776

NSC5936

CHEMBL18549

NSC3712

J2G84H29AF

O0038

CTK0H6650

NE10661

n-C6H13COCH3

RP19810

UNII-J2G84H29AF

2-octanone(Methyl Hexyl Ketone)

HSDB 5545

NSC-3712

NSC 3712

BBL011429

NSC-5936

SBB060387

AK116913

LS-2999

LP003936

2-Octanone (natural)

Jsp000838

STL146536

DTXSID4021927

FEMA Number 2802

A802298

ZINC1672808

CHEBI:87434

KB-69438

CJ-06140

CJ-27197

DA-16705

TRA0044944

AJ-29261

ANW-16240

AN-22644

MFCD00009540

BB_SC-6900

ACN-S002377

ZINC01672808

LMFA12000054

BDBM50028815

TR-002225

ST51046577

ST24031492

RTR-002225

AI3-05617

AKOS005720775

J-002527

I14-5856

FT-0613243

FEMA No. 2802

BRN 0635843

EN300-20060

2-Octanone, reagent grade, 98%

2-Octanone, >=98%, FG

111-13-7

MCULE-1152821440

EINECS 203-837-1

2-Octanone, natural, 98%, FG

MolPort-001-787-588

4-01-00-03339 (Beilstein Handbook Reference)

InChI=1/C8H16O/c1-3-4-5-6-7-8(2)9/h3-7H2,1-2H

The Henry's Law constant for 2-octanone was measured as 1.88X10-4 atm-cu m/mole(1). This Henry's Law constant indicates that 2-octanone 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 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 6 days(SRC). In water, 2-octanone had a measured volatilization flux of 40 g/min/sq m and a gas-film coefficient ratio of 0.554 at 20 deg C, indicating that volatilization from water does occur but that some attenuation of this process may be seen due to the gas-film interface(4). 2-Octanone's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). 2-Octanone is expected to volatilize from dry soil surfaces(SRC), based upon a vapor pressure of 1.35 mm Hg(3).
Literature: (1) Buttery RG et al; J Agric Food Chem 17: 385-9 (1969) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Riddick JA et al; in Organic Solvents: Physical Properties and Methods of Purification. Techniques of Chemistry. 4th ed. NY,NY: Wiley-Interscience. 2: 352 (1986) (4) Rathbun RE, Tai DY; Chemosphere 13: 1009-23 (1984)

The Koc of 2-octanone is estimated as 460(SRC), using a measured log Kow of 2.37(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that 2-octanone is expected to have moderate mobility in soil(SRC).
Literature: (1) Hansch L et al; p. 49 in Exploring QSAR. Hydrophobic, Electronic, and Steric Constants. ACS Prof Ref Book. Amer Chem Soc, Washington, DC (1995) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington DC: Amer Chem Soc pp. 4-9 (1990) (3) Swann RL et al; Res Rev 85: 23 (1983)

Caprinaldehyde

Decanaldehyde

Capraldehyde

DECALDEHYDE

Caprinic aldehyde

KSMVZQYAVGTKIV-UHFFFAOYSA-N

KSMVZQYAVGTKIV-UHFFFAOYSA-

n-DECYLALDEHYDE

Capric aldehyde

Decylic aldehyde

Decanal

n-Decaldehyde

Decyl aldehyde

n-Decanal

Decanal, analytical standard

n-Decyl aldehyde

AC1Q2VYO

AC1L1QFM

1-Decanal

Aldehyde C10

1-Decyl aldehyde

SCHEMBL2540

Decanal (natural)

KSC176G3J

U211

NSC6087

ACMC-1C59Q

C-10 aldehyde

D0032

CTK0H6334

Aldehyde C-10

HSDB 288

31Z90Q7KQJ

WLN: VH9

HMDB11623

NE10468

N-decanal (capric aldehyde)

1-Decanal(mixed isomers)

C12307

UNII-31Z90Q7KQJ

LS-2367

CHEMBL2228377

LP001404

NSC 6087

NSC-6087

DTXSID4021553

SBB058676

Jsp000949

ZINC1693270

A802551

CHEBI:31457

DSSTox_CID_1553

ANW-16447

AN-22691

Natural Decanal(C-10)

KB-49635

EBD2219840

SC-22770

DSSTox_GSID_21553

AK-44487

TRA0073044

MFCD00007031

LMFA06000052

DSSTox_RID_76207

ST24030299

AI3-04860

DB-041074

ST51037233

RTR-002413

TR-002413

AKOS000120018

S14-1463

J-002749

FEMA No. 2362

BRN 1362530

FT-0631643

I14-13645

Decanal, natural, >=97%, FG

Tox21_302656

EN300-20146

112-81-2

112-31-2

decanal (ACD/Name 4.0)

Decanal, >=95%, FCC, FG

NCGC00256769-01

CAS-112-31-2

Decanal, >=98% (GC), liquid

EINECS 203-957-4

MolPort-001-769-696

InChI=1/C10H20O/c1-2-3-4-5-6-7-8-9-10-11/h10H,2-9H2,1H3

The Henry's Law constant for decaldehyde is 1.8x10-3 atm-cu m/mole(1). This Henry's Law constant indicates that decaldehyde 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 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 5 days(SRC). Decaldehyde's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). Decaldehyde is not expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 0.103 mm Hg(3).
Literature: (1) Zhou X, Mopper K; Environ Sci Technol 24: 1482-5 (1990) (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. Washington, DC: Taylor and Francis, (1989)

In water 0.00156 mg/L at 25 deg C
Literature: Yalkowsky, S.H., He, Yan, Jain, P. Handbook of Aqueous Solubility Data Second Edition. CRC Press, Boca Raton, FL 2010, p. 739
Literature: #Soluble in ethanol, ether, acetone; slightly soluble in carbon tetrachloride
Literature: Haynes, W.M. (ed.). CRC Handbook of Chemistry and Physics. 95th Edition. CRC Press LLC, Boca Raton: FL 2014-2015, p. 3-142
Literature: #Soluble in 80% alcohol, fixed oils, volatile oils, mineral oil; insoluble in glycerol
Literature: Lewis, R.J. Sr.; Hawley's Condensed Chemical Dictionary 15th Edition. John Wiley & Sons, Inc. New York, NY 2007., p. 371

Using a structure estimation method based on molecular connectivity indices(1), the Koc of decaldehyde can be estimated to be 70(SRC). According to a classification scheme(2), this estimated Koc value suggests that decaldehyde is expected to have very high mobility in soil.
Literature: (1) US EPA; Estimation Program Interface (EPI) Suite. Ver. 4.1. Nov, 2012. Available from, as of May 20, 2015: http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm (2) Swann RL et al; Res Rev 85: 17-28 (1983)

methylisovalerate

Methyl isovalerianate

Methyl isopentanoate

OQAGVSWESNCJJT-UHFFFAOYSA-N

Methyl isovalerate

Methyl isovalerate, analytical standard

Isovaleric Acid Methyl Ester

Methyl 3-methylbutanoate

Methyl 3-methylbutyrate

Methyl iso-valerate

AC1L1WQS

3-Methylbutanoic acid methyl

Methyl isovalerate (natural)

3-Methylbutanoic acid methyl ester

methyl 3-methyl butanoate

Isovaleric acid, methyl ester

KSC492I1L

UN2400

3-methyl-butyric acid methyl ester

CTK3J2415

METHYL (3-METHYL)BUTANOATE

I0198

SCHEMBL112862

ZINC391144

ACMC-1B229

DTXSID5060300

UN 2400

BBL011395

STL146498

OR019861

LS-2937

ZB011968

OR284399

CHEBI:89832

KB-54994

SC-81704

CJ-03473

AN-45898

ANW-32353

QPS4788198

Methyl isovalerate, >=99%, FG

BB_SC-6790

MFCD00042866

LMFA07010950

ZINC00391144

RT-000613

DB-003722

UNII-QPS4788198

Butanoic acid,3-methyl-, methyl ester

AKOS005721109

BRN 1699922

FEMA No. 2753

FT-0627534

556-24-1

I14-111196

Butanoic acid, 3-methyl-, methyl ester

MCULE-2808202854

Methyl isovalerate, >=98.0% (GC)

Methyl isovalerate [UN2400] [Flammable liquid]

EINECS 209-117-3

MolPort-003-930-982

Methyl isovalerate [UN2400] [Flammable liquid]

4-02-00-00897 (Beilstein Handbook Reference)

InChI=1/C6H12O2/c1-5(2)4-6(7)8-3/h5H,4H2,1-3H

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)