3-ETHYL-5-METHYLPHENOL

698-71-5

m-Cresol, 5-ethyl-

3-Methyl-5-ethylphenol

Phenol, 3-ethyl-5-methyl-

5-Ethyl-m-cresol

1-Hydroxy-3-methyl-5-ethylbenzene

ZV1NMG73ZT

NSC-8885

NSC-62673

NSC 8885

3-ethyl-5-methyl-phenol

UNII-ZV1NMG73ZT

EINECS 211-818-4

NSC 62673

5-Ethyl-3-methylphenol

AI3-24210

5-Ethyl-m-cresol, 8CI

SCHEMBL911575

m-Cresol, 5-ethyl- (8CI)

DTXSID60220101

NSC8885

CHEBI:196443

NSC62673

Phenol, 3-ethyl-5-methyl- (9CI)

AKOS006273528

MCULE-4765819333

AS-57682

DB-074229

A9238

CS-0186818

NS00036977

D84187

Q27295901

6-Chloro-3,7-dimethyl-2H-benzo[e][1,2,4]thiadiazine 1,1-dioxide

M-XYLENE

1,3-Dimethylbenzene

108-38-3

1,3-Xylene

meta-Xylene

m-Xylol

m-Dimethylbenzene

m-Methyltoluene

Benzene, 1,3-dimethyl-

3-Xylene

1,3-Dimethylbenzol

Santosol 150

m-Xylenes

2,4-Xylene

CCRIS 907

NSC 61769

HSDB 135

UNII-O9XS864HTE

EINECS 203-576-3

O9XS864HTE

DTXSID6026298

CHEBI:28488

AI3-08916

NSC-61769

CHEMBL286727

DTXCID501446

EC 203-576-3

M-XYLENE-ALPHA,ALPHA'-13C2

MFCD00008536

68908-87-2

Xylene, m-

Benzene, m-dimethyl-

CAS-108-38-3

EINECS 272-684-0

metaxylene

M xylene

1,3-dimethyl-benzene

m-Xylene [UN1307] [Flammable liquid]

DSSTox_CID_1446

M-XYLENE [MI]

3-XYLENE [HSDB]

bmse000554

DSSTox_RID_76162

DSSTox_GSID_21446

m-Xylene, analytical standard

BENZENE,1,3-DIMETHYL

WLN: 1R C1

m-Xylene, anhydrous, >=99%

m-Xylene, for synthesis, 99%

DTXSID50178041

m-Xylene, ReagentPlus(R), 99%

NSC61769

m-Xylene 10 microg/mL in Methanol

Tox21_200292

Tox21_202056

Tox21_303203

BDBM50008556

STL268867

m-Xylene 100 microg/mL in Methanol

AKOS000121123

MCULE-9376558510

NCGC00091711-01

NCGC00091711-02

NCGC00091711-03

NCGC00257052-01

NCGC00257846-01

NCGC00259605-01

m-Xylene, SAJ first grade, >=98.5%

CAS-1330-20-7

NS00010709

NS00125194

S0648

X0013

EN300-24548

m-Xylene, puriss. p.a., >=99.0% (GC)

C07208

J-503933

Q3234708

F1908-0174

InChI=1/C8H10/c1-7-4-3-5-8(2)6-7/h3-6H,1-2H

m-Xylene, Pharmaceutical Secondary Standard; Certified Reference Material

The Henry's Law constant for 3-xylene is measured as 7.18X10-3 atm-cu m/mole(1). This Henry's Law constant indicates that 3-xylene 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 3.1 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). 3-Xylene's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). 3-Xylene is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 8.29 mm Hg at 25 deg C(3).
Literature: (1) Sanemasa I et al; Bull Chem Soc Jpn 55: 1054-62 (1982) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Chao J et al; J Phys Chem Ref Data 12: 1033-63 (1983)
Literature: #An experiment which measured the rate of evaporation of m- and p-xylene from a 1:1000 jet fuel:water mixture found that it averaged 0.64 times the oxygen reaeration rate(1).
Literature: (1) Smith JH, Harper JC; pp.336-53 in 12th Conf Environ Toxicol: Behavior of Hydrocarbon Fuels in the Aquatic Environment (1980)

A Koc value of 166 was measured for 3-xylene using sandy aquifer materials with an foc ranging from 0.0002 to 0.0225(1). Measured Koc values in soil have been reported to be 182(2), 166 and 275(3). According to a classification scheme(3), these Koc values suggest that 3-xylene is expected to have moderate mobility in soil. A Kp value (equilibrium-sorption coefficient) of 0.049 was measured for 3-xylene using a Borden soil column (98% sand, 0.29% organic carbon)(5). Benzene/toluene/xylene mixtures containing 3-xylene, were added to soil columns using aquifer material from the Cohansey aquifer (90% sand; 4.4% organic matter; pH-3.8); a partition coefficient of 8.74 was measured for 3-xylene(6). Adsorption coefficient values of 0.25, 0.23, and 0.02 were measured for 3-xylene, present in a benzene/toluene/ethylbenzene/xylene mixture, on montmorillonite, illite, and kaolinite (all with low to no organic carbon present), respectively, using a batch equilibrium technique(7). More 3-xylene vapor was sorbed by air-dry than oven-dry soil (Evesham clay; air-dry soil contained 37 g organic C, 350 g clay, and 60 g water/kg oven-dry soil) at relative vapor pressures of 3-xylene exceeding 0.6; this suggests that the planar 3-xylene molecule is either readily adsorbed by interlayer sites in the air-dry soil (more sites potentially available than in oven-dry soil) or, as it is a fairly soluble molecule, that some will dissolve in the water film in air-dry soil(8). 3-Xylene has been observed to pass through soil unchanged in concentration at a dune-infiltration site on the Rhine River(9). A soil leaching column study estimated a 3-xylene Koc of 282 using a chromatographic methodology(10).
Literature: (1) Abdul AS et al; Hazard Waste & Hazard Mater 4: 211-22 (1987) (2) Sabljic A; Environ Sci Technol 21: 358-66 (1987) (3) Schuurmann G et al; Environ Sci Technol 40: 7005-7011 (Supporting information) (2006) (4) Swann RL et al; Res Rev 85: 17-28 (1983) (5) Hu Q et al; Environ Toxicol Chem 14: 1133-40 (1995) (6) Uchrin CG, Katz J; Bull Environ Contam Toxicol 46: 534-41 (1991) (7) Li Y, Gupta G; Chemosphere 28: 627-38 (1994) (8) Nye PH et al; J Environ Qual 23: 1031-37 (1994) (9) Piet GJ et al; Quality of Groundwater Int Symp Proc Von Duijvanbouden W et al, eds. Studies Environ Sci 17: 557-64 (1981) (10) Xu F et al; J Environ Qual 30: 1618-1623 (2001)

toluene

methylbenzene

108-88-3

toluol

Phenylmethane

methacide

methylbenzol

Benzene, methyl-

antisal 1a

Toluen

tolu-sol

Methane, phenyl-

Tolueen

Toluolo

phenyl methane

1-Methylbenzene

monomethyl benzene

RCRA waste number U220

Tolueno

methyl-Benzene

Caswell No. 859

p-toluene

NCI-C07272

CP 25

CCRIS 2366

HSDB 131

NSC 406333

UN 1294

4-methylbenzene

Benzene, methyl

EINECS 203-625-9

UNII-3FPU23BG52

EPA Pesticide Chemical Code 080601

NSC-406333

3FPU23BG52

DTXSID7021360

CHEBI:17578

AI3-02261

TOLUENE (RING-D5)

CHEMBL9113

DTXCID501360

EC 203-625-9

Toluene, anhydrous

MFCD00008512

NCGC00090939-02

TOLUENE (IARC)

TOLUENE [IARC]

TOLUENE (MART.)

TOLUENE [MART.]

TOLUENE (USP-RS)

TOLUENE [USP-RS]

Tolueen [Dutch]

Toluen [Czech]

Toluene, analytical standard

Tolueno [Spanish]

Toluolo [Italian]

methyl benzene

para-toluene

Methyl benzol

Toluene, ACS reagent, >=99.5%

Toluene 1000 microg/mL in Methanol

CAS-108-88-3

RAMIPRIL IMPURITY G (EP IMPURITY)

RAMIPRIL IMPURITY G [EP IMPURITY]

PHME

UN1294

RCRA waste no. U220

methylbenzenes

Dracyl

phenyl-methane

toluene solvent

2-methylbenzene

toluene-

Methylbenzene; Toluene; Ramipril Imp. G (EP); Ramipril Impurity G

MePh

2-methyl benzene

4-methyl-benzene

Toluene ACS Grade

Toluene HPLC grade

Methylbenzene, 9CI

Toluene (Technical)

Toluene, for HPLC

PhCH3

Toluene, ACS reagent

Toluene, HPLC Grade

4i7k

TOLUENE [HSDB]

TOLUENE [INCI]

Toluene, 99.5%

TOLUENE [MI]

CP 25 (SOLVENT)

Toluene, Environmental Grade

Toluene, Semiconductor Grade

Toluene, LR, >=99%

C6H5CH3

TOLUENE [GREEN BOOK]

WLN: 1R

BIDD:ER0288

Toluene, anhydrous, 99.8%

Toluene, ASTM, 99.5%

Toluene, p.a., 99.5%

GTPL5481

Toluene, AR, >=99.5%

Toluene, for HPLC, 99.9%

Toluene, LR, rectified, 99%

CHEBI:38975

DTXSID00184990

DTXSID50175878

Toluene, HPLC grade, 99.8%

Toluene, Spectrophotometric Grade

Toluene 10 microg/mL in Methanol

Toluene, LR, sulfur free, 99%

Toluene, AR, rectified, 99.5%

Toluene, technical grade, 95.0%

BCP16202

Toluene, for HPLC, >=99.8%

Toluene, for HPLC, >=99.9%

Toluene, histology grade, practical

Toluene, PRA grade, >=99.8%

Toluene 100 microg/mL in Methanol

Tox21_111042

Tox21_201224

BDBM50008558

NSC406333

Toluene, purification grade, 99.8%

AKOS015840411

DB11558

MCULE-4817136027

Toluene, anhydrous, (water < 50ppm)

Toluene, puriss., >=99.5% (GC)

Toluene, SAJ first grade, >=99.0%

NCGC00090939-01

NCGC00090939-03

NCGC00258776-01

Toluene [UN1294] [Flammable liquid]

Toluene, JIS special grade, >=99.5%

Toluene, Laboratory Reagent, >=99.3%

Toluene, for HPLC, >=99.7% (GC)

Toluene, UV HPLC spectroscopic, 99.5%

Toluene, anhydrous, ZerO2(TM), 99.8%

DB-309420

NS00008096

T0260

Toluene, suitable for determination of dioxins

C01455

Q15779

Toluene, suitable for scintillation, >=99.7%

Toluene liquid density, NIST(R) SRM(R) 211d

A801937

SR-01000944565

Toluene, ACS spectrophotometric grade, >=99.5%

SR-01000944565-1

Toluene, p.a., ACS reagent, reag. ISO, 99.5%

InChI=1/C7H8/c1-7-5-3-2-4-6-7/h2-6H,1H

D5191 Vapor Pressure - 7.1kPa (1.03 psi), 10 x 10 mL

Toluene, p.a., ACS reagent, reag. ISO, reag. Ph. Eur., 99.5%

Toluene, absolute, over molecular sieve (H2O <=0.005%), >=99.7% (GC)

Toluene, Pharmaceutical Secondary Standard; Certified Reference Material

Residual Solvent - Toluene, Pharmaceutical Secondary Standard; Certified Reference Material

Toluene, puriss. p.a., ACS reagent, reag. ISO, reag. Ph. Eur., >=99.7% (GC)

25013-04-1

The Henry's Law constant for toluene is 6.64X10-3 atm-cu m/mole(1). This Henry's Law constant indicates that toluene 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 2.9 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 3.8 days(SRC). Toluene's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). Toluene is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 28.4 mm Hg(3). The air-water interface equilibrium partitioning coefficient for toluene, at a concentration of 0.47 mg/L, has been reported to be 0.223, 0.226, 0.273, and 0.336 at 26.9, 31.9, 36.9, and 41.9 deg C, respectively(4). A first-order volatilization rate calculated for toluene from water using an inverse reactive simulation was reported as 6.62X10-6/sec(5). The volatilization half-life of toluene from a water column of one meter depth was estimated to be 5.18 hours(6). Toluene was reported to have a disappearance half-life of <2 days due to volatilization in two different soil types, a Captina silt loam and a McLaurin sandy loam(7).
Literature: (1) Mackay D et al; Environ Sci Technol 13: 333-6 (1979) (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) (4) Cheng W-H et al; Atmos Environ 37: 4807-4815 (2003) (5) Keefe SH et al; Environ Sci Technol 38: 2209-2216 (2004) (6) Mackay D, Leinonen PJ; Environ Sci Technol 9: 1178-80 (1975) (7) Anderson TA et al; J Environ Qual 20:420-4 (1991)

The Koc of toluene was reported as 178 in a sandy soil(1) and as 37 (Wendover silty loam), 160 (Grimsby silt loam), 160 (Vaudreil sandy loam) and 46 (sandy soil)(2). The Koc of toluene in lake sediment was measured as 166(3). According to a classification scheme(4), these measured Koc values suggest that toluene is expected to have high to moderate mobility in soil.
Literature: (1) Wilson JT et al; J Environ Qual 10: 501-6 (1981) (2) Nathwani JS, Phillips CR; Chemosphere 6: 157-62 (1977) (3) Kan AT et al; Environ Sci Technol 32: 892-902 (1998) (4) Swann RL et al; Res Rev 85: 17-28 (1983)
Literature: #In association with clay minerals, toluene's adsorption is inversely proportional to the pH of the soil. Approximately 40-70% of toluene applied to the surface of sandy soils is volatilized.
Literature: IARC. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans. Geneva: World Health Organization, International Agency for Research on Cancer, 1972-PRESENT. (Multivolume work). Available at: http://monographs.iarc.fr/ENG/Classification/index.php, p. V47: 90 (1989)

1-Phenyl-1-propyne

673-32-5

Prop-1-yn-1-ylbenzene

Prop-1-ynylbenzene

Benzene, 1-propynyl-

Methylphenylacetylene

1-Phenylpropyne

phenylpropyne

1-Propynylbenzene

Prop-1-ynyl-benzene

MFCD00009272

1-Methyl-2-phenylacetylene

CHEMBL105998

448376BFQC

53621-07-1

1-Phenylpropyne-1

UNII-448376BFQC

Methylphenylethyne

Phenylmethylacetylene

EINECS 211-607-7

1-penyl-1-propine

1-phenyl-1-propine

Propyne, 1-phenyl-

(prop-1-yn-1-yl)benzene

ghl.PD_Mitscher_leg0.471

1-Phenyl-1-propyne, 99%

DTXSID10217667

BDBM50026185

AKOS015888271

CS-W013608

MCULE-3601815161

CS-17361

SY048557

DB-055018

NS00042390

P0219

D71012

EN300-315540

Q27258719

InChI=1/C9H8/c1-2-6-9-7-4-3-5-8-9/h3-5,7-8H,1H

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)

carbon dioxide

carbonic anhydride

Dry ice

124-38-9

carbonic acid gas

Carbonic acid anhydride

Carbonica

Kohlendioxyd

Kohlensaure

Khladon 744

After-damp

AER Fixus

Anhydride carbonique

Carbon oxide, di-

methanedione

CO2

Caswell No. 163

HSDB 516

Dioxido de carbono

Dioxyde de carbone

dioxidocarbon

R 744

Dioxomethane

Cardice

Drikold

EINECS 204-696-9

UN1013

UN1845

UN2187

Carbon-12 dioxide

EPA Pesticide Chemical Code 016601

INS NO.290

UNII-142M471B3J

CHEBI:16526

Carbon oxide (CO2)

Dry ice (solid form)

Carbon dioxide [USP]

INS-290

E-290

142M471B3J

E290

DTXSID4027028

Carbon dioxide (USP)

E 290

CARBON DIOXIDE (II)

CARBON DIOXIDE [II]

18923-20-1

CARBON DIOXIDE (MART.)

CARBON DIOXIDE [MART.]

Kohlensaure [German]

Kohlendioxyd [German]

(CO2)

[CO2]

CARBON DIOXIDE (EP IMPURITY)

CARBON DIOXIDE [EP IMPURITY]

CARBON DIOXIDE (EP MONOGRAPH)

CARBON DIOXIDE [EP MONOGRAPH]

Dioxide, Carbon

CARBON DIOXIDE (USP MONOGRAPH)

CARBON DIOXIDE [USP MONOGRAPH]

Dioxyde de carbone [French]

Anhydride, Carbonic

Dioxido de carbono [Spanish]

Anhydride carbonique [French]

18983-82-9

carbondioxide

epoxyketone

Dricold

carbon dioxid

dry-ice

Dioxomethane #

methane, dioxo-

Carbon dioxide, refrigerated liquid

Carbonic acid, gas

Makr carbon dioxide

Dry ice .

Carbon dioxide (TN)

CARBON-DIOXIDE

Carbon Dioxide Refrigerated

CARBON DIOXIDE [MI]

CARBON DIOXIDE [FCC]

CARBON DIOXIDE [JAN]

Carbon dioxide (JP17/USP)

CARBON DIOXIDE [HSDB]

CARBON DIOXIDE [INCI]

Carbon dioxide, >=99.8%

CARBON DIOXIDE [VANDF]

DTXCID507028

CARBON DIOXIDE [WHO-DD]

CHEMBL1231871

BDBM10856

CARBON DIOXIDE, COMPRESSED

Carbon dioxide, solid or dry ice

CARBON DIOXIDE [GREEN BOOK]

Carbonic dioxide (Refrigerated liquid)

DB09157

UN 1013

UN 1845

UN 2187

USEPA/OPP Pesticide Code: 016601

Carbon dioxide, puriss., >=99.998%

NS00076302

Q1997

R-744

C00011

Carbon dioxide [UN1013] [Nonflammable gas]

Carbon dioxide, Messer(R) CANgas, 99.995%

D00004

Carbon dioxide, solid or dry ice [UN1845] [Class 9]

Carbon dioxide (99.8%), cylinder of 14 L, analytical standard

Carbon dioxide (99.8%), cylinder of 48 L, analytical standard

Carbon dioxide, refrigerated liquid [UN2187] [Nonflammable gas]

4-HYDROXY-3-METHYL-2-BUTANONE

3393-64-4

4-Hydroxy-3-methylbutan-2-one

2-Butanone, 4-hydroxy-3-methyl-

4-Hydroxy-3-methyl-butan-2-one

3-(Hydroxymethyl)-2-butanone

MFCD00004739

2-Butanone, 4-hydroxy-3-methyl-, (+)-

EINECS 222-238-6

AI3-04080

SCHEMBL422046

VVSRECWZBBJOTG-UHFFFAOYSA-

DTXSID80871018

CHEBI:167070

NSC62078

NSC 62078

NSC-62078

AKOS006227961

AS-6244

DA-06692

SY296786

CS-0132490

NS00049948

G29751

EN300-7138115

4-Hydroxy-3-methyl-2-butanone, 65%, technical grade

InChI=1/C5H10O2/c1-4(3-6)5(2)7/h4,6H,3H2,1-2H3

3-Methylanisole

100-84-5

1-Methoxy-3-methylbenzene

3-Methoxytoluene

m-Methylanisole

Benzene, 1-methoxy-3-methyl-

m-Cresol methyl ether

M-METHOXYTOLUENE

Anisole, m-methyl-

Methyl m-tolyl ether

m-Cresyl methyl ether

Methyl m-cresyl ether

3-Methylmethoxybenzene

Methyl 3-methylphenyl ether

1-Methyl-3-methoxybenzene

1-Methoxy-3-methyl-benzene

3-Methyl-1-methoxybenzene

NSC 6255

3-Cresol methyl ether

UI9I3Y6WTZ

CHEMBL349791

NSC-6255

META-CRESOL DEUTEROMETHYL ETHER

EINECS 202-893-4

UNII-UI9I3Y6WTZ

AI3-19476

m-Methyl anisole

3-methyl anisole

Meta-Methylanisole

3-methoxy toluene

3-Methylanisole, 99%

META METHOXYTOLUENE

SCHEMBL12353

DTXSID2051500

SCHEMBL12015250

AMY5179

NSC6255

CHEBI:167079

STR09347

BDBM50008537

MFCD00008395

AKOS000121157

MCULE-7649681864

DB-012728

CS-0034591

M0151

NS00005982

EN300-26366

H11854

A800280

W-108936

Q27291091

Z53834440

F0001-0028

InChI=1/C8H10O/c1-7-4-3-5-8(6-7)9-2/h3-6H,1-2H

STYRENE

Ethenylbenzene

100-42-5

Vinylbenzene

Phenylethylene

Styrol

Benzene, ethenyl-

Cinnamene

Phenylethene

Styrolene

Phenethylene

Styrene monomer

9003-53-6

Vinylbenzol

Vinyl benzene

Styropol SO

Styren

Styrole

Benzene, vinyl-

Ethylene, phenyl-

Vinylbenzen

Stirolo

Styreen

Cinnamenol

Cinnamol

Vinyl-benzene

Bulstren K-525-19

Annamene

NCI-C02200

FEMA No. 3233

FEMA Number 3234

Styrol [German]

CCRIS 564

NSC 62785

Cinnaminol

HSDB 171

EINECS 202-851-5

UNII-44LJ2U959V

25086-18-4

DTXSID2021284

CHEBI:27452

AI3-24374

MAOMIN SM

44LJ2U959V

trans-Styrene-(beta)-d

NSC-62785

STYRENE-ALPHA-13C

STYRENE-BETA,BETA-D2

DTXCID501284

Benzene, (1Z)-ethenyl-2-d-

Styrol (German)

EC 202-851-5

TTB 7302

MFCD00084450

Styrene-d5(StabilizedwithHydroquinone)

12770-88-6

Diarex hf 77

NCGC00091056-01

STYRENE-ALPHA,2,3,4,5,6-D6

STYRENE (IARC)

STYRENE [IARC]

Styreen [Dutch]

Styren [Czech]

Styrene, analytical standard

Stirolo [Italian]

Benzene-d5, ethenyl-d3-

Vinylbenzen [Czech]

Vinylbenzen [Dutch]

6911-81-5

Styron

Styrene 100 microg/mL in Methanol

MFCD00008612

styrene, monomer

Monomer, Styrene

MFCD00044231

Styrene (monomer)

CAS-100-42-5

COLESTYRAMINE IMPURITY A (EP IMPURITY)

COLESTYRAMINE IMPURITY A [EP IMPURITY]

Vinylbenzene, inhibited

Phenylethylene, inhibited

UN2055

Styrene monomer, inhibited

ethenyl-benzene

phenyl-ethylene

p-vinyl benzene

Styron (Salt/Mix)

Ethenylbenzene, 9CI

Styropol (Salt/Mix)

Styropor (Salt/Mix)

PhCH=CH2

STYRENE [HSDB]

STYRENE [INCI]

Styrene, >=99%

STYRENE [MI]

Diarex hf 77 (Salt/Mix)

UN 2055 (Salt/Mix)

WLN: 1U1R

BIDD:ER0247

CHEMBL285235

NSC62785

Styrene, ReagentPlus(R), 99.9%

Tox21_113245

Tox21_200808

STL283958

Styrene 2000 microg/mL in Methanol

Styrene 5000 microg/mL in Methanol

AKOS000119972

MCULE-4715354738

Styrene, SAJ first grade, >=99.0%

NCGC00091056-02

NCGC00091056-03

NCGC00091056-04

NCGC00091056-05

NCGC00258362-01

BP-13451

SY061549

Styrene Solution 0.0001 Wt% in Toluene

DB-244813

diameter 0.05 - 0.1um ,2.5% w/v

NS00010820

S0651

EN300-19671

C07083

C19506

Q28917

Styrene (stabilized with 4-tert-Butylcatechol)

A800199

Styrene, 99.5% stab. with 4-tert-Butylcatechol

Styrene contains 4-tert-Butylcatechol as stabilizer

F1908-0130

Z104474664

Styrene monomer, inhibited [UN2055] [Flammable liquid]

InChI=1/C8H8/c1-2-8-6-4-3-5-7-8/h2-7H,1H

Styrene, ReagentPlus(R), contains 4-tert-butylcatechol as stabilizer, >=99%

98444-30-5

The Henry's Law constant for styrene is reported as 2.75X10-3 atm-cu m/mole(1). This Henry's Law constant indicates that styrene is expected to volatilize from water surfaces(2). Under laboratory conditions, 50% of 2 to 10 mg styrene per liter (depth not specified) was lost by volatilization in 1 to 3 hrs in lake water samples and in 6 to 7 hrs in distilled water, respectively(3). In other studies, the level of styrene in water samples fell from 23 to 3.3 and 0.4 mg/L in 2 hrs and 7 days, respectively, and from 46 to 12.5 and 1.5 mg/L in 2 hrs and 10 days, respectively(4). These findings are relevant to surface waters but not to deeper waters(4). The volatilization half-life of styrene in Rhine River water was 14 days(5). Volatilization of styrene from moist soil surfaces would be slower than in water(4). Samples at 1.5 cm deep of a loamy soil, 26% of 2 mg/kg styrene added volatilized in 31 days(3). The transfer to the air was even slower and less extensive from deep soil(4). The potential for volatilization of styrene from dry soil surfaces may exist(SRC) based upon a vapor pressure of 6.4 mm Hg(6).
Literature: (1) Bocek K; Experimetia, Suppl 23: 231-40 (1976) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Fu MH, Alexander M; Environ Sci Technol 26: 1540-4 (1992) (4) Alexander M; Crit Rev Env Sci Technol 27: 383-410 (1997) (5) Zoeteman BCJ et al; Chemosphere 9: 231-49 (1980) (6) Chao J et al; J Phys Chem Ref Data 12: 1033-63 (1983)

The log Koc of styrene is reported to be 2.96(1). According to a classification scheme(2), this Koc value suggests that styrene is expected to have low mobility in soil. More than 85% of styrene is sorbed in 78 hrs on samples from a sandy aquifer(3). Styrene is retained by particulates particularly in organic matter-rich soils(3). Of styrene that had been allowed to sorb for 3 days, 61.0 and 66.7% was desorbed in 16 days from soil and aquifer soils, respectively(4).
Literature: (1) Schuurmann G et al; Environ Sci Technol 40: 7005-11 (2006) (2) Swann RL et al; Res Rev 85: 17-28 (1983) (3) Fu MH, Alexander M; Environ Sci Technol 26: 1540-4 (1992) (4) Fu MH et al; Environ Toxicol Chem 13: 749-53 (1994)

Benzo[b]thiophene

Thianaphthene

1-Benzothiophene

95-15-8

BENZOTHIOPHENE

Benzothiofuran

Thionaphthene

1-Thiaindene

Thianaphtene

Thianaphthen

1-benzothiophen

BENZO(B)THIOPHENE

Benzothiophen

Benzothiophene-5-D

2,3-Benzothiophene

11095-43-5

Benzo[b]thiophene-D6

MFCD00005864

NSC 47196

CHEMBL87112

CHEBI:35858

NSC-47196

073790YQ2G

13730-27-3

C8H6S

Thianaftene

Thianapthene

UNII-073790YQ2G

hydrobenzothiophene

benzo[b]-thiophene

EINECS 202-395-7

Thianaphthene, 95%

Thianaphthene, 98%

AI3-15523

THIANAPHTHENE [MI]

SCHEMBL7023

BIDD:GT0845

DTXSID2052736

CS-D1193

NSC47196

BDBM50167948

GEO-00284

MFCD31699976

STK053859

AKOS005258172

MCULE-7277751906

PS-5775

SY246286

AM20041456

B0093

NS00020042

EN300-36787

A845195

A847764

Q419709

Q-100899

F0001-2267

Z370711590

InChI=1/C8H6S/c1-2-4-8-7(3-1)5-6-9-8/h1-6

1,2,4-Trimethoxybenzene

135-77-3

Benzene, 1,2,4-trimethoxy-

Hydroxyhydroquinone trimethyl ether

3KU3WD07SS

CHEMBL1668605

DTXSID5035163

MFCD00008360

EINECS 205-219-7

UNII-3KU3WD07SS

EPA Pesticide Chemical Code 040515

AI3-20797

2,4,5-trimethoxybenzene

1,3,4-trimethoxy benzene

SCHEMBL481491

DTXCID3015163

AGIQIOSHSMJYJP-UHFFFAOYSA-

1,2,5-TRIMETHOXYBENZENE

1,3,4-TRIMETHOXYBENZENE

1,2,4-Trimethoxybenzene, 97%

CHEBI:167092

STR04198

Tox21_300993

TRIMETHOXYBENZENE, 1,2,4-

BDBM50336489

AKOS015851701

CS-W017803

PS-5199

NCGC00164023-01

NCGC00164023-02

NCGC00254895-01

AC-23662

CAS-135-77-3

SY014691

1,2,4-BENZENETRIOL TRIMETHYL ETHER

DB-038069

AM20050161

NS00024400

T1130

EN300-187594

F11207

A806985

W-108257

Q27257439

Z1255382978

InChI=1/C9H12O3/c1-10-7-4-5-8(11-2)9(6-7)12-3/h4-6H,1-3H3

1,4-Dimethoxybenzene

150-78-7

p-Dimethoxybenzene

p-Methoxyanisole

HYDROQUINONE DIMETHYL ETHER

Benzene, 1,4-dimethoxy-

Benzene, p-dimethoxy-

Quinol dimethyl ether

Dimethylhydroquinone ether

4-Methoxyanisole

Dimethyl ether hydroquinone

1,4-Dimethoxybenzol

USAF AN-9

Dimethyl hydroquinone

Anisole, p-methoxy-

Methyl p-methoxyphenyl ether

1,4-dimethoxy-benzene

Dimethylether hydrochinonu

USAF uctl-1791

Hydroquinone, dimethyl ether

1,4-dimethoxy benzene

FEMA No. 2386

NSC 7483

Dimethylolbenzimidazolon

MFCD00008401

1,4-Dimethoxybenzene-D6

4-Methoxyphenol, methyl ether

24WC6T6X0G

1,3-Bis(hydroxymethyl)-2-benzimidazolinone

DTXSID0022014

NSC-7483

DTXCID102014

CAS-150-78-7

CCRIS 5920

HSDB 4259

Dimethylether hydrochinonu [Czech]

EINECS 205-771-9

UNII-24WC6T6X0G

AI3-24139

p-Methoxy-Anisole

p-dimethoxy benzene

p-Dimethoxy-Benzene

para-dimethoxybenzene

Hydroquinone dimethyl

PDMXE

1,4-di-methoxybenzene

p-Xylene dimethyl ether

hydroquinone dimethylether

para-dimethyl hydroquinone

EC 205-771-9

1-Methoxy-4-methoxybenzene

SCHEMBL8489

Methyl 4-methoxyphenyl ether

WLN: 1OR DO1

MLS002454408

BENZENE,1,4-DIMETHOXY

CHEMBL1668604

SCHEMBL12015220

BDBM36302

NSC7483

P-DIMETHOXYBENZENE [FHFI]

CHEBI:179261

HMS2270C23

1,4-Dimethoxybenzene, 99%, FG

STR02500

WLN: T56 BNVNJ B1Q D1Q

Tox21_201333

Tox21_302782

STK065405

AKOS000119956

CS-W016496

HY-W015780

MCULE-5232933383

NCGC00091220-01

NCGC00091220-02

NCGC00091220-03

NCGC00256564-01

NCGC00258885-01

1,4-Dimethoxybenzene, analytical standard

HYDROQUINONE DIMETHYL ETHER [HSDB]

PD158325

SMR001252207

2-Benzimidazolinone,3-bis(hydroxymethyl)-

DB-013768

1, 3-Bis(hydroxymethyl)-2-benzimidazolinone

D0629

NS00002609

1,4-Dimethoxybenzene, ReagentPlus(R), 99%

EN300-16130

D70298

1,4-Dimethoxybenzene Hydroquinone dimethyl ether

A809075

Q4545697

W-108072

1,4-Dimethoxybenzene, Vetec(TM) reagent grade, 98%

Z53833835

F1908-0181

InChI=1/C8H10O2/c1-9-7-3-5-8(10-2)6-4-7/h3-6H,1-2H

1,4-Dimethoxybenzol; 4-Methoxyanisole; DMB;Hydroquinone Dimethyl Ether; Methyl 4-Methoxyphenyl Ether

42500-66-3

The Henry's Law constant for hydroquinone dimethyl ether is estimated as 3.5X10-3 atm-cu m/mole(1,SRC). This value indicates that hydroquinone dimethyl ether may volatilize from water surfaces(2,SRC). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec) is estimated as approximately 4 hours(2,SRC). The volatilization half-life from a model lake (1 m deep) is estimated as approximately 5 days(2,SRC).
Literature: (1) Meylan W, 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 p. 15-1 to 15-29 (1990)

Based on an experimental log Kow of 2.03(1), the Koc of hydroquinone dimethyl ether is estimated as approximately 300 using a regression-derived equation(2,SRC). According to a suggested classification scheme(3), this estimated Koc value suggests that hydroquinone dimethyl ether will have moderate mobility in soil(SRC).
Literature: (1) Hansch C et al; Exploring QSAR: Hydrophobic, Electronic, and Steric Constants. ACS Profess Ref Book, Washington,DC: Amer Chem Soc (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)

4-Methylanisole

1-METHOXY-4-METHYLBENZENE

104-93-8

p-Methylanisole

4-Methoxytoluene

p-Methoxytoluene

Benzene, 1-methoxy-4-methyl-

p-methyl anisole

p-Cresol methyl ether

p-Cresyl methyl ether

Anisole, p-methyl-

4-Methyl anisole

Methyl p-cresol

Methyl p-tolyl ether

p-Tolyl methyl ether

Methyl p-cresyl ether

para-Methylanisole

1-Methyl-4-methoxybenzene

4-Methyl-1-methoxybenzene

4-Methylphenol methyl ether

Methyl 4-methylphenyl ether

Methyl-para-cresol

para-Methoxytoluene

Methyl p-methylphenyl ether

p-methylanisol

para-Cresyl methyl ether

para-methyl anisole

1-Methoxy-4-methyl-benzene

FEMA No. 2681

4-Methylanizole

NSC 6254

para-Methyl anisol

4-methylmethoxybenzene

4-METHOXYTOLUENE-D7

10FAI0OR9W

CHEMBL154155

DTXSID9026710

CHEBI:89728

NSC-6254

4-methylanisol

Toluene, 4-methoxy-

FEMA Number 2681

PARA-CRESOL DEUTEROMETHYL ETHER

HSDB 5363

EINECS 203-253-7

UNII-10FAI0OR9W

AI3-07621

p- methylanisole

p-Methyl-Anisole

p-Methoxy toluene

4-methoxy-toluene

MFCD00008413

VANADIUMGALLIDE

4-Methylanisole (MSO)

P- METHOXYTOLUENE

4-Methylanisole, 99%

1-methyoxy-4-methylbenzene

EC 203-253-7

SCHEMBL12464

4-CRESOL METHYL ETHER

WLN: 1OR D1

P-METHYLANISOLE [FHFI]

DTXCID306710

SCHEMBL2489775

P-METHYL ANISOLE [FCC]

SCHEMBL12015216

FEMA 2681

AMY5180

NSC6254

4-Methylanisole, analytical standard

Tox21_201081

BDBM50008555

STL268886

AKOS000121016

4-Methylanisole, >=99%, FCC, FG

CS-W013551

HY-W012835

MCULE-8571139509

NCGC00248917-01

NCGC00258634-01

1-METHOXY-4-METHYLBENZENE [HSDB]

BS-23266

CAS-104-93-8

PD164982

M0149

NS00010202

EN300-16112

W-108799

Q15726084

Z53834227

F0001-0094

InChI=1/C8H10O/c1-7-3-5-8(9-2)6-4-7/h3-6H,1-2H

The Henry's Law constant for 1-methoxy-4-methylbenzene is estimated as 4.7X10-3 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This value indicates that 1-methoxy-4-methylbenzene will volatilize from water surfaces(2,SRC). 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) is estimated as approximately 3.4 hours(2,SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec) is estimated as approximately 4.4 days(2,SRC). 1-Methoxy-4-methylbenzene's vapor pressure, 1.1 mm Hg(3,SRC) and Henry's Law constant(1,SRC) indicate that volatilization from dry and moist soil may occur(SRC).
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)

INSOL IN WATER; SOL IN ETHER, ETHANOL, AND CHLOROFORM.
Literature: Lide, D.R. (ed.). CRC Handbook of Chemistry and Physics. 75th ed. Boca Raton, Fl: CRC Press Inc., 1994-1995., p. 3-54
Literature: #1:3 IN 80% ALCOHOL, 1:7 IN 70% ALCOHOL
Literature: Fenaroli's Handbook of Flavor Ingredients. Volume 2. Edited, translated, and revised by T.E. Furia and N. Bellanca. 2nd ed. Cleveland: The Chemical Rubber Co., 1975., p. 346

The Koc of 1-methoxy-4-methylbenzene is estimated as approximately 670(SRC), using an experimental log Kow of 2.66(1) and a regression-derived equation(2,SRC). According to a recommended classification scheme(3), this estimated Koc value suggests that 1-methoxy-4-methylbenzene has low mobility in soil(SRC).
Literature: (1) Hansch C et al; Exploring QSAR. Hydrophobic, Electronic, and Steric Constants. ACS Professional Reference Book. Heller SR (consult ed) Washington, DC: Amer Chem Soc (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)