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36934

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Bis(methylglycol) phthalate

analytical standard

Synonyme(s) :

Bis(2-methoxyethyl) phthalate, Dimethylglycol phthalate

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About This Item

Formule empirique (notation de Hill):
C14H18O6
Numéro CAS:
117-82-8
Poids moléculaire :
282.29
Numéro Beilstein :
2056929
Numéro CE :
204-212-6
Numéro MDL:
MFCD00042842
Code UNSPSC :
41116107
ID de substance PubChem :
329755546
Nomenclature NACRES :
NA.24

Qualité

analytical standard

Niveau de qualité

100

Durée de conservation

limited shelf life, expiry date on the label

Technique(s)

HPLC: suitable
gas chromatography (GC): suitable

Point d'ébullition

230 °C/10 mmHg (lit.)

Densité

1.173 g/mL at 20 °C (lit.)

Application(s)

cleaning products
cosmetics
environmental
food and beverages
personal care

Format

neat

Chaîne SMILES 

COCCOC(=O)c1ccccc1C(=O)OCCOC

InChI

1S/C14H18O6/c1-17-7-9-19-13(15)11-5-3-4-6-12(11)14(16)20-10-8-18-2/h3-6H,7-10H2,1-2H3

Clé InChI

HSUIVCLOAAJSRE-UHFFFAOYSA-N

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Description générale

Bis(methylglycol) phthalate belongs to the class of phthalate esters widely used as plasticizers in plastic films.

Application

Refer to the product′s Certificate of Analysis for more information on a suitable instrument technique. Contact Technical Service for further support. Bis(methylglycol) phthalate may be used as an analytical reference standard for the quantification of the analyte in plastic food packaging materials using gas chromatography coupled to tandem mass spectrometry.

Produits recommandés

Find a digital Reference Material for this product available on our online platform ChemisTwin® for NMR. You can use this digital equivalent on ChemisTwin® for your sample identity confirmation and compound quantification (with digital external standard). An NMR spectrum of this substance can be viewed and an online comparison against your sample can be performed with a few mouseclicks. Learn more here and start your free trial.

Pictogrammes

Health hazard
GHS08

Mention d'avertissement

Danger

Mentions de danger

H360

Classification des risques

Repr. 1B

Code de la classe de stockage

6.1C - Combustible acute toxic Cat.3 / toxic compounds or compounds which causing chronic effects

Classe de danger pour l'eau (WGK)

WGK 1

Point d'éclair (°F)

249.8 °F - closed cup

Point d'éclair (°C)

121 °C - closed cup

Équipement de protection individuelle

Eyeshields, Gloves, type ABEK (EN14387) respirator filter

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Certificats d'analyse (COA)

Lot/Batch Number
BCCK8840
BCCB3394
BCBT9573
BCBT5847
SZBD193XV

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Si vous avez besoin d'une version particulière, vous pouvez rechercher un certificat spécifique par le numéro de lot.

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Gas chromatography-triple quadrupole tandem mass spectrometry for successive single-surface migration study of phthalate esters from polythene film
Yang J, et al.
Food Control, 73, 1134-1143 (2017)
M R Parkhie et al.
Environmental health perspectives, 45, 89-97 (1982-11-01)
A single intraperitoneal injection (0.6 ml/kg) of dimethoxyethyl phthalate (DMEP) was given to groups of Wistar strain rats on day 10, 11, 12, 13 or 14 of gestation. Control rats received 0.6 ml/kg of physiological saline intraperitoneally. In phthalate-treated rats
Yuki Ito et al.
Journal of occupational health, 49(3), 172-182 (2007-06-19)
Di(2-ethylhexyl)phthalate (DEHP), a commonly used industrial plasticizer, causes liver tumorigenesis presumably via activation of peroxisome proliferator-activated receptor alpha (PPARalpha). The mechanism of DEHP tumorigenesis has not been fully elucidated, and to clarify whether DEHP tumorigenesis is induced via PPARalpha, we
E J Ritter et al.
Teratology, 32(1), 25-31 (1985-08-01)
It is hypothesized that the known teratogen di(2-methoxyethyl) phthalate (DMEP) acts by in vivo hydrolysis to 2-methoxyethanol (2-ME), also a known teratogen, which in turn is metabolized to methoxyacetic acid (MAA), the proximate teratogen. Teratological studies were conducted with Wistar
Wataru Naito et al.
Environmental monitoring and assessment, 115(1-3), 451-471 (2006-05-02)
Screening-level ecological risk assessments of di(2-ethylhexyl)phthalate (DEHP) for aquatic organisms in Japan were conducted using estimated statistical values based on surface water and sediment monitoring data and effect threshold values based on a large aquatic toxicity database. An alternative method
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