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EC number: 203-603-9 | CAS number: 108-65-6
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data

Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- September 6, 2001
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted according to the Principles of GLP and the report contains sufficient information to permit a meaningful evaluation of study results
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 001
- Report date:
- 2001
Materials and methods
- Objective of study:
- other: in vitro hydrolysis and kinetics
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- The aim of this study were to determine the in vitro rates of hydrolysis of PGMEA to PGME in whole blood from rats and humans as well as the half-life for hydrolysis in liver homogenate from rats and humans. Another aim was to determine the blood kinetics of PGMEA and PGME following intravenous administration to Fischer 344 rats.
- GLP compliance:
- yes
Test material
- Reference substance name:
- 2-methoxy-1-methylethyl acetate
- EC Number:
- 203-603-9
- EC Name:
- 2-methoxy-1-methylethyl acetate
- Cas Number:
- 108-65-6
- Molecular formula:
- C6H12O3
- IUPAC Name:
- 2-methoxy-1-methylethyl acetate
- Details on test material:
- - Name of test material (as cited in study report): Propylene Glycol Monomethyl Ether Acetate (PGMEA) and Propylene Glycol Monomethyl Ether (PGME)
- Physical state: liquid
- Analytical purity: for PGMEA, 99.32% . For PGME: 99.63%
- Isomers composition: not specified in the report
- Lot/batch No.: PGMEA: The Dow Chemical Company, Midland, Michigan (OA17019G04), PGME: Aldrich, Milwaukee, Wisconsin (OB1001B101)
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories for non-cannulated animals and Hilltop Lab Animals, Inc. for jugular vein cannulated animals
- Age at study initiation: approximately 10 weeks old
- Weight at study initiation: 191-210 g
- Fasting period before study: not specified in the report
- Housing: Non-cannulated animals were housed two per cage in stainless steel cages and jugular vein cannulated animals were housed individually
- Individual metabolism cages: yes
- Diet (e.g. ad libitum): LabDiet Certified Rodent Diet #5002 in pelleted form provided ad libitum
- Water (e.g. ad libitum): Municipal water provided ad libitum
- Acclimation period: Non-cannulated animals were acclimated to the laboratory environment for at least one-week prior to use. Jugular vein cannulated rats were acclimated in metabolism cages for one day prior to use.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21-25 °C
- Humidity (%): 38-48%
- Air changes (per hr): 12-15 times/hour
- Photoperiod (hrs dark / hrs light): 12-hour light/dark photocycle
Administration / exposure
- Route of administration:
- intravenous
- Vehicle:
- physiological saline
- Details on exposure:
- PREPARATION OF INTRAVENOUS DOSING SOLUTIONS: For dose solutions administered intravenously, PGME or PGMEA was weighed directly in a tared vial and physiological saline was added to reach final concentrations of 5 mg PGME/ml or 7.35 mg PGMEA/ml. Similarly for the higher concentrations, PGME or PGMEA was weighed directly in a tared vial and physiological saline was added to reach final concentrations of 50 mg PGME/ml or 73.5 mg PGMEA/ml.
All dose solutions were within 90-101% of their targeted concentrations. For targeted PGME doses of 10 or 100 mg/kg, the actual mean values were
10.72 or 99.57 mg/kg, respectively. For targeted PGMEA doses of 14.7 or 147 mg/kg, the actual mean values were 16.83 or 142.42 mg/kg, respectively. - Duration and frequency of treatment / exposure:
- 12 hour(s)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Males: 10 and 100 mg PGME/kg body weight
Males: 14.7 and 147 mg PGMEA/kg body weight
- No. of animals per sex per dose / concentration:
- Males: four cannulated rats/group
- Control animals:
- no
- Positive control reference chemical:
- not applicable
- Details on study design:
- - Dose selection rationale: based on previously conducted studies
- Rationale for animal assignment: randomly assigned to treatment groups using a computer-driven randomization procedure - Details on dosing and sampling:
- Blood samples of about 0.1 ml each were drawn from the jugular cannula 5, 10, 15, 30, 45 minutes, and 1, 2, 4, 6, 8, 12 hours post dosing using a heparinized syringe.
- Statistics:
- All data based calculations were conducted using Microsoft Excel with full precision (Microsoft Corporation, 1998). Descriptive statistics were calculated mean +/- standard deviation (SD) for all sets of data collected during the study. The in vivo concentration time course of PGME and PGMEA in plasma was described by a noncompartmental model using the method of residuals and linear regression to estimate the half-life (PK Solutions, Summit Research Services, Ashland, Ohio). PK Solutions was also used to estimate rates of hydrolysis for PGMEA in the in vitro studies.
Results and discussion
Metabolite characterisation studies
- Metabolites identified:
- not measured
- Details on metabolites:
- not measured
Any other information on results incl. tables
Plasma time courses of PGME in rats following intravenous administration of a low-dose of PGME or PGMEA were indistinguishable, within experimental error of the measurements. For the high-dose of PGME or PGMEA, time courses of PGME were also identical. Half-lives for PGME following administration of a low-dose of PGME or PGMEA were 8.1 and 10.4 minutes, respectively. These data are in agreement with a probe study, where the half-life was determined to be 5.72 minutes following IV administration of 10 mg PGMEA/kg bw.
Plasma time courses of PGMEA in rats following intravenous administration of 14.7 or 147 mg PGMEA/kg bw were determined. Half-lives were 1.55 and 3.37 minutes following intravenous administration of the low- and high-dose, respectively. These data are in agreement with a probe study, where the half-life was determined to be 2.2 minutes following IV administration of 50 mg PGMEA/kg bw.
The in vitro hydrolysis rates of PGMEA in rat and human blood and liver homogenates were investigated in incubations at concentrations of 5 and 50 μg/ml. Hydrolysis half-lives were calculated through 60 minutes from time courses of PGMEA in rat or human blood spiked with 5 or 50 μg PGMEA/ml incubation mixture. The disappearance of PGMEA from blood was faster by ~2 fold in rat blood than in human blood. In rat blood, PGMEA was hydrolyzed in 15-16 minutes and in human blood the hydrolysis half-lives ranged from 34-36 minutes.
Hydrolysis half-lives were calculated through 60 minutes from time courses of PGMEA in rat or human liver homogenate spiked with 5 or 50 μg PGMEA/ml incubation mixture. The disappearance of PGMEA from rat liver homogenates was very similar in rat and human incubations. The in vitro hydrolysis half-lives ranged from 28-34 minutes.
In summary, data from this study support
rapid hydrolysis of PGMEA in vivo and once hydrolyzed, the kinetics of
PGME derived from the ester PGMEA are identical to the kinetics for
PGME. The findings also support the existing toxicology database on
PGMEA. Since PGMEA was not detected in the plasma or urine of rats
exposed to PGMEA via inhalation indicates that the parent chemical is
very rapidly and extensively hydrolyzed, presumably via tissue and
plasma carboxylesterases. In studies by Stott and McKenna, 1984 and
1985, and Miller 1984, PGME and PGMEA vapors were extensively absorbed
by the upper respiratory tract and PGMEA was shown to be a substrate for
nasal carboxylesterase in an in vitro study.
Applicant's summary and conclusion
- Conclusions:
- PGME was injected intravenously to rats at dose of 10 and 100 mg/kg . Blood samples were collected up to 12 hours post exposure to determine kinetic parameters. PGMA was also tested with the same experimental procedures in order to determine kinetic differences between the two substances. Half lives of blood PGME were 10.36 and 38.62 min for the low and high dose respectively
- Executive summary:
For investigation of the kinetics of PGME or PGMEA following intravenous administration via the jugular vein cannula, equimolar doses of 10 mg PGME/kg or 14.7 mg PGMEA/kg and 100 mg PGME or 147 mg PGMEA/kg were used. Blood samples were drawn from the jugular vein cannula at 5, 10, 15, 30, 45 minutes and 1, 2, 4, 6, 8, and 12 hours post-dosing. The samples were analyzed via PCI+EI-GC/MS for determination of PGMEA and PGME.
Plasma time course of PGME in rats following intravenous administration of 10 mg PGME/kg bw or 14.7 mg PGMEA/kg bw were
identical. For the high-dose of 100 mg PGME/kg or 147 mg PGMEA/kg, time courses of PGME were also identical.
Plasma time courses of PGMEA in rats following intravenous administration of 14.7 or 147 mg PGMEA/kg bw were determined. Half lives were 1.55 and 3.37 minutes following intravenous administration of the low- and high-dose, respectively.
The in vitro hydrolysis rates of PGMEA in rat and human blood and liver homogenates were investigated in incubations at concentrations of 5 and 50 μg/ml. Hydrolysis half-lives were calculated through 60 minutes from time courses of PGMEA in rat or human blood spiked with 5 or 50 μg PGMEA/ml incubation mixture. The disappearance of PGMEA from blood was faster by ~2 fold in rat blood than in human blood. In rat blood, PGMEA was hydrolyzed in 15-16 minutes and in human blood the hydrolysis half-lives ranged from 34-36 minutes.
Hydrolysis half-lives were calculated through 60 minutes from time courses of PGMEA in rat or human liver homogenate spiked with 5 or 50 μg PGMEA/ml incubation mixture. The disappearance of PGMEA from rat liver homogenates was very similar in rat and human incubations. The in vitro hydrolysis half-lives ranged from 28-34 minutes.
In summary results from these studies as well as from earlier studies indicate that propylene glycol monomethyl ether acetate is rapidly hydrolyzed in the body to its parent glycol ether, propylene glycol monomethyl ether. Once hydrolyzed the kinetics for PGME derived from PGMEA is identical to that for PGME.
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