Results for:
PubChem ID: 7929

1,3-xylene

Mass-Spectra

Compound Details

Synonymous names
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
Microorganism:

Yes

IUPAC name1,3-xylene
SMILESCC1=CC(=CC=C1)C
InchiInChI=1S/C8H10/c1-7-4-3-5-8(2)6-7/h3-6H,1-2H3
FormulaC8H10
PubChem ID7929
Molweight106.16
LogP3.2
Atoms8
Bonds0
H-bond Acceptor0
H-bond Donor0
Chemical Classificationaromatic compounds alkylbenzenes benzenoids
CHEBI-ID28488
Supernatural-IDSN0156540

mVOC Specific Details

Boiling Point
DegreeReference
139.1 °C peer reviewed
Volatilization
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)
Soil Adsorption
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)
Vapor Pressure
PressureReference
8.29 mm Hg at 25 deg CChao J et al; J Phys Chem Ref data 12: 1033-63 (1983)
MS-Links
1D-NMR-Links
Massbank-Links

Species emitting the compound
KingdomSpeciesBiological FunctionOrigin/HabitatReference
EukaryotaAspergillus NigerNANACosta et al. 2016
EukaryotaCandida AlbicansNANACosta et al. 2016
EukaryotaPenicillium ChrysogenumNANACosta et al. 2016
ProkaryotaPseudomonas Pseudoalcaligenespromotes the growth of Zea mays L. and confer the resistance to drought stress in this maizeApplied Microbiology and Biotechnology lab, Department of Biosciences, Comsats University IslamabadYasmin et al. 2021
EukaryotaTuber Excavatumn/aFortywoodland of the Basilicata regionMauriello et al. 2004
EukaryotaTuber Borchiin/aFortywoodland of the Basilicata regionMauriello et al. 2004
EukaryotaTuber Brumalen/aFortywoodland of the Basilicata regionMauriello et al. 2004
EukaryotaTuber Aestivumn/aAgricultural Centre of Castilla and León Community (Monasterio de la Santa Espina, Valladolid, Spain) and Navaleno (Soria, Spain).Diaz et al. 2003
EukaryotaPaecilomyces Variotiinacompost, soils, food productsSunesson et al. 1995
ProkaryotaPseudomonas Sp.NANAEtminani et al. 2022
ProkaryotaLentilactobacillus BuchneriNANASquara et al. 2022
ProkaryotaLacticaseibacillus ParacaseiNANASquara et al. 2022
Fusarium GraminearumBallot et al. 2023
MicrobacteriumBallot et al. 2023
Method
KingdomSpeciesGrowth MediumApplied MethodVerification
EukaryotaAspergillus NigerYeast Glucose ChloramphenicolSPME/GCxGC-MSno
EukaryotaCandida AlbicansYeast Glucose ChloramphenicolSPME/GCxGC-MSno
EukaryotaPenicillium ChrysogenumYeast Glucose ChloramphenicolSPME/GCxGC-MSno
ProkaryotaPseudomonas PseudoalcaligenesLB mediaSPME/GC-MSno
EukaryotaTuber Excavatumn/amicroextraction-gas chromatography-mass spectrometry analysis (SPME-GC-MS)no
EukaryotaTuber Borchiin/amicroextraction-gas chromatography-mass spectrometry analysis (SPME-GC-MS)no
EukaryotaTuber Brumalen/amicroextraction-gas chromatography-mass spectrometry analysis (SPME-GC-MS)no
EukaryotaTuber Aestivumn/aHeadspace solid-phase microextraction (HS-SPME) combined with GC-MSno
EukaryotaPaecilomyces VariotiiDG18,MEAGC/MSno
ProkaryotaPseudomonas Sp.nutrient agar (NA)GC–MSno
ProkaryotaLentilactobacillus Buchnerimaize silageHS-SPME coupled with GC-TOF MSno
ProkaryotaLacticaseibacillus Paracaseimaize silageHS-SPME coupled with GC-TOF MSno
Fusarium Graminearumtryptone soy (TS medium; Carl Roth, Karlsruhe, Germany)GC-QQQ-MSno
Microbacteriumtryptone soy (TS medium; Carl Roth, Karlsruhe, Germany)GC-QQQ-MSno