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)

Dimethylethylene glycol

Pseudobutylene glycol

Sym-dimethylethylene glycol

OWBTYPJTUOEWEK-UHFFFAOYSA-N

Dimethylene glycol

AC1Q2BQD

AC1L18UG

2,3-Dihydroxybutane

ACMC-1BUD7

KSC270E6J

ACMC-209euy

2,3-butanodiol

2,3-butanediol

7110AF

HMDB03156

2,3-Butandiol

B0681

CTK1H0264

ACMC-209gb6

2,3-butylene glycol

2,3-dihydroxy butane

2,3-dihydroxy-butane

RL03891

DL-2,3-Butanediol

A18844

CCRIS 5501

HSDB 1505

D-2,3-BUTANEDIOL

CHEMBL2312529

Butane-2,3-diol

OR035318

OR332866

OR094911

DL-2,3-BUTANDIOL

DTXSID8041321

2,3- butanediol

NSC249246

2,3-butane diol

Butan-2,3-diol

CHEBI:62064

SC-81338

LS-45795

levo-butane-2,3-diol

KB-67232

SC-08971

SC-08972

DSSTox_GSID_41321

ANW-41590

AN-23501

MFCD00004523

DSSTox_CID_21321

DSSTox_RID_79687

2D-PHARMALYTE (9CI)

TR-032024

NSC-249246

D-2,3-Butane diol

RTR-032024

DB-027533

AKOS009031391

FT-0696715

BRN 0969165

I14-19052

Z966690926

2,3-Butanediol (DL)

PROPOXY, 2-HYDROXY-1-METHYL-

Tox21_300789

2,3-Butanediol, 98%

2,3-BUTANEDIOL, 96%

513-85-9

NCGC00248169-01

NCGC00254693-01

CAS-513-85-9

EINECS 208-173-6

2,3-Butanediol, analytical standard, mixture of racemic and meso forms

35007-63-7

98923-25-2

123513-85-9

MolPort-003-927-421

2,3-Butanediol, Vetec(TM) reagent grade, 98%

4-01-00-02524 (Beilstein Handbook Reference)

2,3-Butanediol, [R-(R*,R*)]-

2,3-Butanediol, purum, mixture of racemic and meso forms, >=98.0% (GC)

2,3-Butanediol, puriss., mixture of racemic and meso forms, >=99.0% (GC)

2,3-Butanediol, (R*,R*)-(.+/-.)-

InChI=1/C4H10O2/c1-3(5)4(2)6/h3-6H,1-2H

The Henry's Law constant for 2,3-butanediol is estimated as 2.9X10-8 atm-cu m/mole(SRC) derived from its vapor pressure, 0.24 mm Hg(1), and an assigned value for water solubility of 1.0X10+6 mg/L (miscible)(2). This Henry's Law constant indicates that 2,3-butanediol is expected to be essentially nonvolatile from water surfaces(3). 2,3-Butanediol is not expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure of 0.24 mm Hg(1).
Literature: (1) NIST; Chemistry WebBook. National Institute of Standards and Technology Standard Reference Database Number 69 - March 2003 Release, Available from the query page at http://webbook.nist.gov/chemistry as of Mar 3, 2005. (2) Riddick JA et al; Techniques of Chemistry. 4th ed. Vol II. Organic Solvents. NY, NY: John Wiley and Sons p. 270 (1985) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990)

The Koc of 2,3-butanediol is estimated as 7.5(SRC), using a log Kow of -0.92(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that 2,3-butanediol is expected to have very 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. 10 (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)

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)

RSJKGSCJYJTIGS-UHFFFAOYSA-N

Hendecane

Hendekan

Undecane

undecan

Undekan

undecyl group

Undecane, analytical standard

n-Hendecane

UND

N-UNDECANE

JV0QT00NUE

UNII-JV0QT00NUE

UNDECAN-2-YL

U203

AC1L23G2

Decane, methyl-

KSC176C3J

UN2330

Undecane, >=99%

U0002

QSPL 058

S0283

CTK0H6134

Undecane, 99%

NSC66159

CHEMBL132474

ACMC-209t6p

HSDB 5791

CCRIS 3796

LTBB002321

LP077622

LP067812

LP092643

Jsp000912

n-C11H24

UN 2330

DTXSID9021689

ZINC1693211

CHEBI:46342

DSSTox_CID_1689

NSC 66159

TRA0090240

SC-79237

DSSTox_GSID_21689

CC-33184

NSC-66159

ANW-42095

AN-20593

C-28174

DSSTox_RID_76285

MFCD00008959

LMFA11000591

RTR-002350

AI3-21126

TR-002350

DB-041031

LS-158394

AKOS005145675

J-002689

FT-0633353

BRN 1697099

I14-60624

Tox21_300076

CH3-[CH2]9-CH3

NCGC00254001-01

NCGC00247896-01

MCULE-7319807036

1120-21-4

EINECS 214-300-6

n-Undecane, 99% 50g

Undecane [UN2330] [Flammable liquid]

61193-21-3

CAS-1120-21-4

MolPort-001-783-218

Undecane [UN2330] [Flammable liquid]

4-01-00-00487 (Beilstein Handbook Reference)

17398EC4-D16F-42F6-8A27-60F8EC075469

InChI=1/C11H24/c1-3-5-7-9-11-10-8-6-4-2/h3-11H2,1-2H

The Henry's Law constant for n-undecane is estimated as 6.1 atm-cu m/mole(SRC) derived from its vapor pressure, 0.412 mm Hg(1), and water solubility, 0.014 mg/L(2). This Henry's Law constant indicates that n-undecane 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 3.6 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). However, volatilization from water surfaces is expected to be attenuated by adsorption to suspended solids and sediment in the water column. The estimated volatilization half-life from a model pond is about 1 month if adsorption is considered(4). n-Undecane's estimated Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). n-Undecane is not expected to volatilize from dry soil surfaces based upon its vapor pressure(SRC).
Literature: (1) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals Data Compilation. Washington, DC: Taylor and Francis (1999) (2) Shaw DG; Hydrocarbons with Water and Seawater. Part II: Hydrocarbons C8 to C36. International Union of Pure and Applied Chemistry. Solubility Data Series. Vol 38 p. 326 (1989) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington,DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (4) USEPA; EXAMS II Computer Simulation (1987)

In water, 0.014 mg/L at 25 deg (critical evaluation of all available data)
Literature: Shaw DG; Hydrocarbons with Water and Seawater. Part II: Hydrocarbons C8 to C36. International Union of Pure and Applied Chemistry. Solubility Data Series. Vol 38 p. 326 (1989)
Literature: #In water, 0.0044 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. 806
Literature: #Miscible with ethyl alcohol, ether
Literature: Haynes, W.M. (ed.). CRC Handbook of Chemistry and Physics. 95th Edition. CRC Press LLC, Boca Raton: FL 2014-2015, p. 3-544

Using a structure estimation method based on molecular connectivity indices(1), the Koc of n-undecane can be estimated to be 2,600(SRC). According to a classification scheme(2), this estimated Koc value suggests that n-undecane is expected to have slight mobility in soil.
Literature: (1) US EPA; Estimation Program Interface (EPI) Suite. Ver. 4.11. Nov, 2012. Available from, as of Nov 16, 2015: http://www2.epa.gov/tsca-screening-tools (2) Swann RL et al; Res Rev 85: 23 (1983)

Tetramethylpyrazin

TETRAMETHYLPYRAZINE

Chuanxiongzine

chuanxingzine

Ligustrazine

Liqustrazine

Tetrapyrazine

Ligustizine

FINHMKGKINIASC-UHFFFAOYSA-

FINHMKGKINIASC-UHFFFAOYSA-N

TMPZ

Bs factor

Pyrazine, tetramethyl-

PubChem8617

V80F4IA5XG

AC1L23J7

H601

KSC491G1N

ZINC4042

CT0189

SCHEMBL77624

UNII-V80F4IA5XG

CTK3J1316

N1918

2,5,6-Tetramethylpyrazine

ACMC-2099er

CHEMBL303697

NSC36080

NSC46451

FEMA 3237

HMS2235K03

HMS3371J08

BBL012277

BT000139

DTXSID6047070

HE000625

HE143578

HE296334

LS-3117

Opera_ID_849

SBB085945

STL163591

SY011353

ZB000557

A802574

M-4966

AC-10515

AJ-08191

AK-47432

AN-20604

ANW-16465

BR-47432

CJ-00093

DSSTox_GSID_47070

KB-81076

NSC 36080

NSC 46451

NSC-36080

NSC-46451

SC-43874

TRA0067329

ACN-S003305

BB_NC-2565

CHEBI:133246

DSSTox_CID_27070

DSSTox_RID_82085

MFCD00006146

ZINC00004042

2,3,5,6-Tetramethylpyrazine

AM20070299

CCG-207974

DB-003786

RTR-002428

ST24032257

ST45025457

TR-002428

AKOS003398567

I14-0730

Q-100069

FEMA No. 3237

FT-0609443

MLS000069594

Nat.2,3,5,6-Tetramethylpyrazine

SMR000059042

2,3,5,6-Tetramethylpyrazine, analytical standard

2,3,5,6-Tetramethyl pyrazine

2,3,5,6-Tetramethyl-pyrazine

Tox21_302313

Z1741976694

1124-11-4

MCULE-2834033564

NCGC00247063-01

NCGC00256097-01

2,3,5,6-Tetramethylpyrazine (natural)

EINECS 214-391-2

Pyrazine, 2,3,5,6-tetramethyl

87396-75-6

93615-56-6

CAS-1124-11-4

2,3,5,6-Tetramethylpyrazine, 98%

MolPort-002-473-658

Pyrazine, 2,3,5,6-tetramethyl-

AC-907/25014219

76494-51-4 (hydrochloride)

2,3,5,6-TETRAMETHYL-1,4-PYRAZINE

2,3,5,6-Tetramethylpyrazine, >=98%, FG

2,3,5,6,-Tetramethyl-1,4-pyrazine

2,3,5,6-Tetramethylpyrazine, natural, >=98%, FG

2,3,5,6-Tetramethylpyrazine, Vetec(TM) reagent grade, 98%

InChI=1/C8H12N2/c1-5-6(2)10-8(4)7(3)9-5/h1-4H3

DIOQZVSQGTUSAI-UHFFFAOYSA-N

DECANE

decan

Decyl hydride

Dekan

normal-decane

decyl group

Decane, analytical standard

AC1Q2VXY

n-Decane

n-Dekan

ACMC-1BUCN

D10

AC1L268C

HSDB 63

I932

KSC179Q2P

N-DECANE, CERTIFIED GRADE

Nonane, methyl-

C10H22

decan-2-yl

decan-3-yl

decan-5-yl

NSC8781

UN2247

CCRIS 653

CTK0H9827

D0011

Decane, >=95%

NK85062OIY

QSPL 111

S0282

S0554

CHEMBL134537

Decane, 99%

Decane, n-

LS-693

RP20784

LTBB002320

UNII-NK85062OIY

WLN: 10H

Decane, anhydrous, >=99%

DTXSID6024913

Jsp001609

LP003952

LP004138

LP067944

LP068261

LP092567

n-C10H22

NSC 8781

NSC-8781

STL280316

UN 2247

CHEBI:41808

DSSTox_CID_4913

Reference Material for Flash Point Certified by The Japan Petroleum Institute, Decane

ZINC1648227

AN-22946

ANW-42089

DSSTox_GSID_24913

KB-49638

SC-79309

TRA0023373

DSSTox_RID_77577

LMFA11000568

MFCD00008954

AI3-24107

RTR-003754

TR-003754

AKOS005145676

Alkanes, C10-18

J-005051

J-520211

BRN 1696981

FT-0697465

Decane, ReagentPlus(R), >=99%

I14-17989

Tox21_201881

Tox21_300336

(C10-C18) Alkanes

124-18-5

F1908-0171

CH3-[CH2]8-CH3

Decane, SAJ special grade, >=99.0%

MCULE-6071426098

NCGC00247996-01

NCGC00247996-02

NCGC00254283-01

NCGC00259430-01

CAS-124-18-5

EINECS 204-686-4

28598-83-6

63335-87-5

73138-29-1

n-Decane, 99% 100ml

MolPort-001-783-724

n-Decane [UN2247] [Flammable liquid]

Decane, purum, >=95.0% (GC)

Decane, purum, >=98.0% (GC)

n-Decane [UN2247] [Flammable liquid]

4-01-00-00464 (Beilstein Handbook Reference)

DBF497D1-4529-4457-841E-9D33CDF22B1C

InChI=1/C10H22/c1-3-5-7-9-10-8-6-4-2/h3-10H2,1-2H

The Henry's Law constant for n-decane is estimated as 5.15 atm-cu m/mole(SRC) derived from its vapor pressure, 1.43 mm Hg(1), and water solubility, 0.052 mg/L(2). This Henry's Law constant indicates that n-decane 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 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)(3) is estimated as 4.7 days(SRC). n-Decane's estimated Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). n-Decane is expected to volatilize from dry soil surfaces based upon its vapor pressure(SRC). Biodegradation studies in soil have observed volatilization to be a more important removal process than biodegradation for n-decane(4,5).
Literature: (1) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals. Design Inst Phys Prop Data, Amer Inst Chem Eng. New York, NY: Hemisphere Pub. Corp. (1989) (2) Yalkowsky SH et al; Handbook of Aqueous Solubility Data. 2nd ed., Boca Raton, FL: CRC Press, p. 745 (2010) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (4) Stronguilo ML et al; Chemosphere 29: 272-81 (1994) (5) Dean-Ross D; Bull Environ Contam Toxicol 51: 596-9 (1993)
Literature: #First-order evaporation constants of n-decane in 3-mm layer No 2 fuel oil, darkened room, wind speed 21 km/hr: at 5 deg C, 1.19X10-3/min; at 10 deg C, 1.87X10-3/min; at 20 deg C, 3.44X10-3/min; at 30 deg C, 6.98X10-3/min
Literature: Verschueren, K. Handbook of Environmental Data on Organic Chemicals. Volumes 1-2. 4th ed. John Wiley & Sons. New York, NY. 2001, p. 655

Using a structure estimation method based on molecular connectivity indices(1), the Koc of n-decane can be estimated to be 1500(SRC). According to a classification scheme(2), this estimated Koc value suggests that n-decane is expected to have low mobility in soil.
Literature: (1) US EPA; Estimation Program Interface (EPI) Suite. Ver. 4.11. Nov, 2012. Available from, as of Nov 9, 2015: http://www2.epa.gov/tsca-screening-tools (2) Swann RL et al; Res Rev 85: 17-28 (1983)