Propylbenzene

N-PROPYLBENZENE

103-65-1

1-Phenylpropane

Phenylpropane

Isocumene

Benzene, propyl-

1-Propylbenzene

n-Propyl benzene

Propylbenzene, n-

propyl benzene

Propyl-benzene

NSC 16941

HSDB 5353

UNII-0WR86ZHG2Z

EINECS 203-132-9

0WR86ZHG2Z

DTXSID3042219

CHEBI:42630

AI3-23862

NSC-16941

CHEMBL286062

DTXCID1022219

Propylbenzene, analytical standard

UN2364

Propylbenzene (all isomers)

benzene, propyl

3H0

Benzene, n-propyl-

PRPH

Propylbenzene, 98%

BENZENE,PROPYL

PROPYLBENZENE [MI]

PHENYLPROPANE [INCI]

WLN: 3R

N-PROPYLBENZENE [HSDB]

Propylbenzene, >=99.0% (GC)

NSC16941

Tox21_300567

BDBM50167945

MFCD00009377

AKOS000120950

MCULE-1436126757

UN 2364

NCGC00248093-01

NCGC00254532-01

CAS-103-65-1

n-Propylbenzene 100 microg/mL in Methanol

NS00006753

P0523

S0656

EN300-20607

n-Propyl benzene [UN2364] [Flammable liquid]

A800778

Q288806

J-001016

J-523764

Z104479154

InChI=1/C9H12/c1-2-6-9-7-4-3-5-8-9/h3-5,7-8H,2,6H2,1H

The Henry's Law constant for n-propylbenzene is 1.05X10-2 atm-cu m/mole(1). This Henry's Law constant indicates that n-propylbenzene 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 1 hour(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 days(SRC). Results of mesocosm studies simulating the Narragansett Bay indicate that volatilization is the major removal process from seawater(3); volatilization half-lives of 1.3-19 days were estimated for summer, spring and winter seasons(5). n-Propylbenzene's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of n-propylbenzene from dry soil surfaces may exist(SRC) based upon it's vapor pressure of 3.42 mm Hg(4).

A Koc of 725 was measured for n-propylbenzene using a surface sediment collected from the Tamar estuary(1). A similar Koc of 676 was measured in a humic acid column via HPLC(2). Adsorption percentages ranging from 0.16 to 5.58% were measured in soil column studies using three different soil types and a sludge sample(3). Using a structure estimation method based on molecular connectivity indices(4), the Koc for n-propylbenzene can be estimated to be 955(SRC). According to a classification scheme(5), these estimated and measured Koc values suggest that n-propylbenzene is expected to have low mobility in soil.

MESITYL OXIDE

141-79-7

4-Methylpent-3-en-2-one

4-Methyl-3-penten-2-one

3-Penten-2-one, 4-methyl-

Methyl isobutenyl ketone

Isopropylideneacetone

Isobutenyl methyl ketone

Mesityloxid

Mesityloxyde

Ossido di mesitile

3-Isohexen-2-one

Isopropylidene acetone

Oxyde de mesityle

Acetone, isopropylidene-

Methyl 2-methyl-1-propenyl ketone

Methyl 2,2-dimethylvinyl ketone

2-Methyl-4-oxo-2-pentene

2-Methyl-2-pentenone-4

2,2-Dimethylvinyl methyl ketone

4-Metil-3-penten-2-one

4-Methyl-3-pentene-2-one

4-Methyl-3-penten-2-on

2-Methyl-2-penten-4-one

FEMA No. 3368

NSC 38717

4-Methyl-3-penten-2-one, 9CI

4-methyl-pent-3-en-2-one

DTXSID1029170

CHEBI:89993

(CH3)2C=CHC(=O)CH3

NSC-38717

77LAC84669

DTXCID209170

Mesityloxid [German]

Mesityloxyde [Dutch]

Caswell No. 547

FEMA Number 3368

Oxyde de mesityle [French]

CAS-141-79-7

Ossido di mesitile [Italian]

HSDB 1195

EINECS 205-502-5

4-Metil-3-penten-2-one [Italian]

UN1229

EPA Pesticide Chemical Code 052401

BRN 1361550

4-Methyl-3-penten-2-on [Dutch, German]

AI3-07702

UNII-77LAC84669

Mesityloxid(german)

MFCD00008900

Isopropylidene-Acetone

Mesityl oxide [UN1229] [Flammable liquid]

EC 205-502-5

2-methylpent-2-en-4-one

MESITYL OXIDE [MI]

1-Methylpent-2-en-4-one

MESITYL OXIDE [HSDB]

CHEMBL3185916

FEMA 3368

WLN: 1Y1 & U1V1

4-Methyl-3-penten-2-one, 90%

AMY23356

NSC38717

Tox21_202080

Tox21_303606

LMFA12000030

STL146350

Mesityl oxide, technical grade, 90%

AKOS000118892

MCULE-4922478422

UN 1229

NCGC00249161-01

NCGC00257514-01

NCGC00259629-01

4-Methyl-3-penten-2-one (mesityl oxide)

4-Methyl-3-penten-2-on(DUTCH, GERMAN)

4-METHYL-3-PENTENE-2-ONE [FHFI]

M0069

M1340

NS00006985

TEICOPLANIN IMPURITY A [EP IMPURITY]

3-PENTEN,2-ONE,4-METHYL MESITYLOXIDE

EN300-21333

Mesityl oxide [UN1229] [Flammable liquid]

3-PENTEN,2-ONE,4-METHYL MESITYLOXIDE

A807813

CILASTATIN SODIUM IMPURITY D [EP IMPURITY]

Q425668

Q-201356

4-Methyl-3-penten-2-one, analytical reference material

Mesityl oxide, 90%, remainder 4-methyl-4-penten-2-one

InChI=1/C6H10O/c1-5(2)4-6(3)7/h4H,1-3H

Mesityl oxide, European Pharmacopoeia (EP) Reference Standard

4-Methylpent-3-en-2-one; Mesityl oxide; Cilastatin Sodium Imp. D (EP)

Mesityl Oxide, Pharmaceutical Secondary Standard; Certified Reference Material

Mesityl oxide, suitable for neutral marker for measuring electroosmotic flow (EOF), ~98%

The Henry's Law constant for mesityl oxide is estimated as 3.67X10-5 atm-cu m/mole(SRC) derived from its vapor pressure, 8.21 mm Hg(1), and water solubility, 28,900 mg/L(2). This Henry's Law constant indicates that mesityl oxide 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 17 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 11 days(SRC). Mesityl oxide's estimated Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of mesityl oxide from dry soil surfaces may exist(SRC) based upon its vapor pressure(1).
Literature: (1) Daubert TE, Danner DP; Physical & Thermodynamic Properties of Pure Chemicals Vol. 3 NY: Hemisphere Pub Corp (1989) (2) Yalkowsky SH, He Y; Handbook of Aqueous Solubility Data. CRC Press LLC, Boca Raton, FL. p. 285 (2003) (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 mesityl oxide is estimated as 15(SRC), using a water solubility of 28,900 mg/L(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that mesityl oxide is expected to have very high mobility in soil.
Literature: (1) Yalkowsky SH, He Y; Handbook of Aqueous Solubility Data. CRC Press LLC, Boca Raton, FL. p. 285 (2003) (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)

cis-6-Tridecene

6-Tridecene

6-Tridecene, (Z)-

(Z)-tridec-6-ene

6508-77-6

6-Tridecene, (6Z)-

(6Z)-6-Tridecene

6-Tridecene, (Z)

548QB57U6U

(Z)-6-Tridecene

UNII-548QB57U6U

Z-6-Tridecene

NSC68824

.ZETA.-CIS-TRIDECENE

CHEBI:88594

DTXSID10880931

QHOMPCGOCNNMFK-QBFSEMIESA-N

24949-38-0

NSC-68824

NS00096273

Q27160483

octane

n-octane

111-65-9

Oktan

Oktanen

Ottani

n-Oktan

Oktanen [Dutch]

Oktan [Polish]

Ottani [Italian]

HSDB 108

UNII-X1RV0B2FJV

X1RV0B2FJV

NSC 9822

EINECS 203-892-1

DTXSID0026882

CHEBI:17590

AI3-28789

NSC-9822

MFCD00009556

DTXCID406882

CH3-[CH2]6-CH3

EC 203-892-1

Heptane, methyl-

Octane, all isomers

CH3-(CH2)6-CH3

octano

Normal octane

normal-Octane

octan

Octanes

Octil

MG8

OTTANE

OCTANE [INCI]

N-OCTANE [HSDB]

OCTANE [MI]

bmse000480

Octane, analytical standard

WLN: 8H

Octane, anhydrous, >=99%

Octane, reagent grade, 98%

n-C8H18

Octane, p.a., 99.0%

CHEMBL134886

NSC9822

Octane; NSC 9822; n-Octane

Tox21_202452

c0044

LMFA11000002

AKOS015904009

MCULE-3248084959

NCGC00249228-01

NCGC00260001-01

CAS-111-65-9

LS-13532

NS00006444

O0022

O0118

O0151

Octane, puriss. p.a., >=99.0% (GC)

C01387

Q150681

J-002613

F0001-0244

EEE64B73-0375-4303-AFD5-0795361807FF

InChI=1/C8H18/c1-3-5-7-8-6-4-2/h3-8H2,1-2H

Octane, electronic grade, >=99.999% metals basis, >=99% (CP)

31372-91-5

9065-92-3

The Henry's Law constant for n-octane is estimated as 3.2 atm-cu m/mole(SRC) derived from its vapor pressure, 14.1 mm Hg(1), and water solubility, 0.66 mg/L(2). This Henry's Law constant indicates that n-octane 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 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 4.2 days(SRC). Volatilization from water surfaces may be attenuated by adsorption to suspended solids and sediment in the water column(SRC). The estimated volatilization half-life from a model pond is 11 months if adsorption is considered(4). However, in a study using a jet fuel mixture and sterile freshwater controls from the Escambia River (Florida), a 99% loss of n-octane was attributed to evaporation at 25 deg C(5). n-Octane's estimated Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). The disappearance of n-octane was rapid in soil/water mixture (concentration of soil, 25 g/150 mL)(6); an initial concentration of 0.177 ug/mL n-octane disappeared completely in 5 days using a sterile sandy loam soil with an organic matter content of 5.1%(6). The potential for volatilization of n-octane from dry soil surfaces may exist(SRC) based upon its vapor pressure(1).
Literature: (1) Yaws CL; Handbook of Vapor Pressure. Houston, TX: Gulf Pub Co. 3: 78 (1994) (2) Yalkowsky SH, He Y, eds; Handbook of aqueous solubility data. Boca Raton, FL: CRC Press p. 536 (2003) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (4) US EPA; EXAMS II Computer Simulation (1987) (5) Spain JC et al; Degrad of Jet Fuel Hydrocarbons by Aquatic Microbial Communities. Tyndall AFB, FL: Air Force Eng Serv Ctr. AFESC/ESL-TR-83-26 (NTIS AD-A139791/8) p 226 (1983) (6) Dean-Ross D; Bull Environ Contam Toxicol 51: 596-99 (1993)

The Koc of n-octane is estimated as 3.1X10+4(SRC), using a log Kow of 5.18(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that n-octane is expected to be immobile in soil. Freundlich absorption coefficients of log 4.04 and log 3.49 were measured in Oberlausitz lignite (11.1% moisture content; 53.5 wt% carbon content; 0.6 wt % nitrogen content) and Pahokee peat soil (10.2% moisture content; 46.1 wt% carbon content; 3.3 wt % nitrogen content), respectively(4). Gaseous transport of volatile n-octane in unsaturated porous media was shown to be influenced by air-water interfacial adsorption and water-partitioning(5). Sorption of n-octane from air to snow was measured, resulting in a sorption coefficient of log -4.41 cu m/sq m at -6.8 deg C(6).
Literature: (1) Miller MM et al; Environ Sci Technol 19:522-9 (1985) (2) US EPA; Estimation Program Interface (EPI) Suite. Ver. 4.1. Nov, 2012. Available from, as of Oct 30, 2013: http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm (3) Swann RL et al; Res Rev 85: 17-28 (1983) (4) Endo S et al; Environ Sci Technol 42): 5897-5903 (2008) (5) Kim H et al; Environ Sci Technol 35: 4457-62 (2001) (6) Roth CM et al; Environ Sci Technol 38: 4078-84 (2004)

Dimethyl disulfide

624-92-0

METHYL DISULFIDE

Dimethyldisulfide

Dimethyl disulphide

DMDS

Disulfide, dimethyl

2,3-Dithiabutane

(Methyldisulfanyl)methane

Methyldisulfide

Methyldithiomethane

(Methyldithio)methane

Sulfa-hitech

dimethyldisulphide

FEMA No. 3536

NSC 9370

1,2-Dimethyldisulfane

CCRIS 2939

HSDB 6400

EINECS 210-871-0

UNII-3P8D642K5E

CHEBI:4608

Dimethyl-d6 disulfide

AI3-25305

3P8D642K5E

NSC-9370

MFCD00008561

DTXSID4025117

(CH3S)2

EC 210-871-0

Paladin

UN2381

dimethydisulfide

methyl disulphide

Dimethyl disulfane

Disulfide dimethyl

MeS-SMe

Disulfide, dimethyl-

methyldisulfanyl methane

Dimethyl disulfide, 98%

Dimethyl disulfide, 99%

(Methyldisulfanyl)methane #

Dimethyl disulfide, >=99%

WLN: 1SS1

DTXCID805117

METHYL DISULFIDE [HSDB]

CHEMBL1347061

Dimethyl disulfide, >=99.0%

DIMETHYL DISULFIDE [FHFI]

NSC9370

BDBM233038

Dimethyl disulfide, >=98%, FG

AMY39506

EINECS 272-923-9

Tox21_201525

AKOS009157459

Dimethyl disulfide, analytical standard

MCULE-7451882535

UN 2381

NCGC00091798-01

NCGC00091798-02

NCGC00259075-01

CAS-624-92-0

Dimethyl disulfide, natural, >=98%, FG

D0714

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

NS00001484

EN300-36043

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

C08371

E78981

A833808

Dimethyl disulfide [UN2381] [Flammable liquid]

Q419800

Q-100719

F0001-1676

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)

ISOPRENE

78-79-5

2-Methyl-1,3-butadiene

2-Methylbuta-1,3-diene

Isopentadiene

2-Methylbutadiene

2-Methyldivinyl

1,3-Butadiene, 2-methyl-

beta-Methylbivinyl

isopreno

isoterpene

Isopren

3-Methyl-1,3-butadiene

CH2=C(CH3)CH=CH2

.beta.-Methylbivinyl

NSC 9237

Naturalrubber

CCRIS 6253

HSDB 620

EINECS 201-143-3

UNII-0A62964IBU

9003-31-0

9006-04-6

DTXSID2020761

NATURAL RUBBER

CHEBI:35194

0A62964IBU

NSC-9237

DTXCID20761

NSC9237

EC 201-143-3

ISOPRENE (IARC)

ISOPRENE [IARC]

Rubber, natural

UN1218

Caoutchouc

Elastomers

Ebonite

Heveaplus

Impervia

Rubber

Latex particles

Nafka

Natural latex

India rubber

Nafka kristalgom

Dynatex LA

Dynatex GTZ

Thiokol NVT

LATZ latex

2-methyl-butadiene

Isoprene, inhibited

Harub 5LV

Heveacrumb SMR 5L

2-methyl-1

Lorival R 25

Hartex 102HR

Cartex 600

Fultite FB 010K

Fultite FB 520

Hartex 103

Fultite FB 3001

Iotex C 60

Isoprene, >=99%

Kagetex FA 2005

ISOPRENE [HSDB]

E 218 (rubber)

Mitsuwa RC paper Cement

ISOPRENE [MI]

Defo 700

Elastic materials, rubber

UNII-2LQ0UUW8IN

Lotol L 9241

2LQ0UUW8IN

Be Be Tex 1223

bmse000844

Defo 1000

ISNA 5

2-methyl-buta-1,3-diene

AMA 7

CSV 1

Isoprene, analytical standard

Mar DR 1135

68877-32-7

UN 1218 (Salt/Mix)

DRC 60

CHEMBL1566132

Isoprene (Stabilized with TBC)

WLN: 1UY1&1U1

HSDB 6772

DTXSID60185761

GLN 200

GNL 150

Isoprene (1 mg/mL in Methanol)

JLX 105

JLX 113

KDP 150

CV 50

CV 60

IR 25

IR 68

AMY37001

EINECS 232-689-0

Tox21_200067

5L-TP0203

CS 700

HC 106

MFCD00008600

AKOS000119971

CCG-266006

FB 3001

CAS-78-79-5

NCGC00091078-01

NCGC00091078-02

NCGC00257621-01

PD088096

I0160

NS00001388

EN300-19669

Q271943

Isoprene, inhibited [UN1218] [Flammable liquid]

J-509898

InChI=1/C5H8/c1-4-5(2)3/h4H,1-2H2,3H

Z104474660

Isoprene, 99%, contains <1000 ppm p-tert-butylcatechol as inhibitor

26796-44-1

9041-65-0

The Henry's Law constant for isoprene is estimated as 0.077 atm-cu m/mole(SRC) derived from its vapor pressure, 550 mm Hg(1), and water solubility, 642 mg/L(2). This Henry's Law constant indicates that isoprene 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 2.4 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 3.3 days(SRC). Isoprene's estimated Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of isoprene from dry soil surfaces may exist(SRC) based upon its vapor pressure(1).
Literature: (1) Zwolinski BJ, Wilhoit RC; Handbook of Vapor Pressures and Heats of Formation of Hydrocarbons and Related Compounds. API44-TRC101 College Station, TX: Thermodynamics Res Ctr p. 48 (1971) (2) McAuliffe C; J Phys Chem 70: 1267-75 (1966) (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 isoprene is estimated as 61(SRC), using a log Kow of 2.42(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that isoprene is expected to have high mobility in soil.
Literature: (1) Chemicals Inspection and Testing Institute. Japan Chemical Industry Ecology - Toxicology and Information Center. ISBN 4-89074-101-1 (1992) (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)

1-TRIDECANOL

Tridecanol

112-70-9

Tridecan-1-ol

Tridecyl alcohol

26248-42-0

n-Tridecan-1-ol

n-Tridecanol

n-Tridecyl alcohol

80206-82-2

1-Hydroxytridecane

MFCD00004756

DTXSID2021947

CHEBI:34123

NSC-5252

8I9428H868

DTXCID901947

N-TRIDECYL-D27 ALCOHOL

CAS-112-70-9

CCRIS 8591

HSDB 5574

NSC 5252

EINECS 203-998-8

BRN 1739991

AI3-35264

UNII-8I9428H868

EINECS 279-420-3

1-Tridecanol, 97%

Maybridge1_004320

SCHEMBL20879

1-TRIDECANOL [HSDB]

BIDD:ER0306

CHEMBL24832

WLN: Q13

TRIDECYL ALCOHOL [INCI]

HMS553M10

AMY5938

NSC5252

BBA24842

Tox21_202208

Tox21_300138

LMFA05000171

STL287936

AKOS005267216

CS-W004293

HY-W004293

MCULE-4385103550

NCGC00164019-01

NCGC00164019-02

NCGC00164019-03

NCGC00254162-01

NCGC00259757-01

1-Tridecanol, purum, >=98.0% (GC)

BP-28084

BS-14333

SY049489

NS00007712

T0803

H10847

EN300-1841776

A894533

Q161684

J-002821

J-016351

85AD1334-FDF8-446D-BF63-A7EE6B26FE07

F0001-0261