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EC number: 220-548-6 | CAS number: 2807-30-9
- 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
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1998
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study methodology followed was equivalent or similar to OECD TG 427 and was conducted in accordance with the Principles of GLP and the report contains sufficient information to permit a meaningful evaluation of study results
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 427 (Skin Absorption: In Vivo Method)
- Deviations:
- yes
- Remarks:
- Some procedures and activities were not fully documented.Some animal room daily environmental records were not located.The animal records(receipt, environmental and lighting) had a significant number of write-overs and other inappropriate corrections to t
- Principles of method if other than guideline:
- The current studies were undertaken to determine the rate and extent of metabolism of Ethylene glycol mono propyl ether [14C]-EGPE following either oral, nose-only inhalation, or dermal exposures, and to determine blood kinetic parameters for EGPE and Propoxy acetic acid (PAA) following exposures by these routes as well as following intravenous administration
- GLP compliance:
- yes
Test material
- Reference substance name:
- 2-(propyloxy)ethanol
- EC Number:
- 220-548-6
- EC Name:
- 2-(propyloxy)ethanol
- Cas Number:
- 2807-30-9
- Molecular formula:
- C5H12O2
- IUPAC Name:
- 2-(propyloxy)ethanol
- Details on test material:
- - Name of test material (as cited in study report): Ethylene glycol mono-propyl ether (EGPE)
- Physical state: liquid
- Analytical purity: 99.9% pure EGPE by capillary gas chromatography.
- Impurities (identity and concentrations): not specified
- Lot/batch No.: not specified
- Radiochemical purity (if radiolabelling): The radiochemical purities for both of these preparations were determined initially to be 97.9 % by packed-column gas chromatography with radiochemical flow detection
- Specific activity (if radiolabelling): Two samples of 2-[ethylene-l ,2-I4C]EGPE ([14C]-EGPE) were obtained from Wizard Laboratories (Davis, CA) wii h specific radioactivities of 8.7 mCi/mmole and 15.3 mCi/mmole.
- Locations of the label (if radiolabelling): not specified
- Expiration date of radiochemical substance (if radiolabelling): not specified
- Stability under test conditions: not specified
- Storage condition of test material: not specified
- Other: Unlabeled Propxyacetic acid (PAA) and Butoxyacetic acid (BAA), required as GC standards, were prepared by reaction of the corresponding sodium salts of n-propanol and n-butanol, respectively, with sodium monochloroacetate. The 14C-labeled acid, [1-14C]propoxyacetic acid, was prepared in a manner similar to that described for the unlabeled acids. The labeled starting material, [1-14C]chloroacetic acid (Sigma Chemical Co., St. Louis, MO), was added along with a large excess of solid sodium monochloroacetate to an excess of the sodium propoxide in anhydrous propanol. The final [14C]-PAA had a specific activity of 8.9 µCi/g and was characterized by capillary-column GC/MS. All other chemicals: were of reagent-grade purity.
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- Two samples of 2-[ethylene-l ,2-I4C]EGPE ([14C]-EGPE) were obtained from Wizard Laboratories (Davis, CA) with specific radioactivities of 8.7 mCi/mmole and 15.3 mCi/mmole
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River
- Age at study initiation: 6-7 weeks of age
- Weight at study initiation: 193-225 g
- Fasting period before study: Feed was withheld for a period of approximately 6-8 hr before and 4 hr after the oral gavage administration.
- Housing: individually housed
- Individual metabolism cages: yes
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 8 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 72 ± 4°F
- Humidity (%): 50 ± 20%
- Air changes (per hr): not specified
- Photoperiod (hrs dark / hrs light): 12 hours light/dark cycle
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- unchanged (no vehicle)
- Duration of exposure:
- single
- Doses:
- For the dermal studies, known weights of unlabeled and radiolabeled EGPE were combined such that nominally 50 mg/cm2 (approximately 450 mg/kg) and 350 µCi/kg of undiluted [14C]-EGPE were applied to the test animals. Dose formulations were prepared on the day prior to treatment
- No. of animals per group:
- 5-10 animals
- Control animals:
- no
- Details on study design:
- DOSE PREPARATION
- Method for preparation of dose suspensions: For the dermal studies, known weights of unlabeled and radiolabeled EGPE were combined such that nominally 50 mg/cm2 (approximately 450 mg/kg) and 350 µCi/kg of undiluted [14C]-EGPE were applied to the test animals.
- Method of storage: Dose formulations were prepared on the day prior to treatment
APPLICATION OF DOSE: Approximately 24 hr prior to the dermal application of the test substance, the dorsal region of rats designated for dermal exposure was shaved with small animal clippers. The following day, a custom-made glass containment cell was attached to the shaved region of each rat. The attachment surface of each containment cell was saddle-shaped and enclosed a 2 cm2 area of the skin. The upper surface of each cell was flat and a polyethylene disc with a central needle hole was adhered to this surface using cyanoacrylate adhesive. The containment cells were cleaned with acetone and allowed to dry thoroughly before attachment to the animals. The cells were positioned along the dorsal midline of each animal and held in place with a cyanoacrylate adhesive. Pressure was applied for approximately 1 min to insure proper adhesion
- Details on in vitro test system (if applicable):
- not applicable
Results and discussion
- Signs and symptoms of toxicity:
- no effects
- Dermal irritation:
- no effects
- Absorption in different matrices:
- as described below
- Total recovery:
- as described below
Percutaneous absorptionopen allclose all
- Dose:
- 0.0549 g/cm2
- Remarks on result:
- other: 72 hours
- Remarks:
- blood: not calculated (radioactivity in tissues and carcasses in male SD rats)
- Dose:
- 0.0549 g/cm2
- Remarks on result:
- other: 72 hours
- Remarks:
- carcass: concentration (43.76 ± 13.69 nmol/g), % dose (0.86 ± 0.25 total tissue) (radioactivity in tissues and carcasses in male SD rats)
- Dose:
- 0.0549 g/cm2
- Remarks on result:
- other: 72 hours
- Remarks:
- kidneys: concentration (54.37 ± 14.45 nmol/g), % dose (0.013 ± 0.0035 total tissue) (radioactivity in tissues and carcasses in male SD rats)
- Dose:
- 0.0549 g/cm2
- Remarks on result:
- other: 72 hours
- Remarks:
- liver: concentration (125.34 ± 32.49 nmol/g), % dose (0.16 ± 0.040 total tissue) (radioactivity in tissues and carcasses in male SD rats)
- Dose:
- 0.0549 g/cm2
- Remarks on result:
- other: 72 hours
- Remarks:
- spleen: concentration (49.81 ± 11.23 nmol/g), % dose (0.003 ± 0.0008 total tissue) (radioactivity in tissues and carcasses in male SD rats)
- Dose:
- 0.0549 g/cm2
- Remarks on result:
- other: 72 hours
- Remarks:
- dermal exposure site: concentration (4209.37 ± 1058.2 nmol/g), % dose (0.49 ± 0.19 total tissue) (radioactivity in tissues and carcasses in male SD rats)
- Conversion factor human vs. animal skin:
- not applicable
Any other information on results incl. tables
Dermal Administration of [Ethylene-UL- 14C]-EGPE
Recovery of radioactivity: Male rats received an average applied dose of 475.5 ± 31.3
mg of EGPE/kg body weight. Based on the amount and the specific activity of the
[14C]-EGPE administered (366.37 µCi/g), this corresponded to a mean administered activity of 42.499 ± 2.006 µCi/rat.
Little of the applied dose was absorbed during the: 6 hr exposure period. A total of 73.5 % of the applied dose was recovered unabsorbed from the site of application following 6 hr of dermal exposure: the liquid dose remaining at the site accounted for 38.3 % of this with the remaining 35.1 % recovered in soap and water ,washings of the application site. Urinary elimination was rapid, with 5.1 % of the administered dose recovered in urine and cage wash samples by 12 hr and a total of 5.50% by 72 hr.
Elimination as 14CO2 accounted for 0.11 % of the applied dose by 72 hr. Most of the radioactivity eliminated as 14CO2 was recovered during the first 12-hr collection period (0.08 %). An additional 0.35 % of the administered dose was recovered from feces and 2.46% as volatile organics. The majority of volatile organics recovered is presumed to represent evaporation of residual EGPE from the exposed dermal sites. At the final
collection period, mean cumulative recovered radioactivity amounted to 83.42% of the
administered dose.
Tissue distribution of residual radioactivity: The highest level of total residual radioactivity was found in carcasses and represented 0.86 % of the administered dose. Lesser amounts of radiolabel were found in the kidneys, livers, spleens, and dermal exposure site and represented 0.013 % , 0.16%, 0.003 % , and 0.49% of the administered dose, respectively, for these samples. The dermal exposure sites contained the highest concentration of residual radioactivity, 4209.4 nmol/g, with far lesser concentrations in the liver (125.3 nmol/g), carcasses (43.8 nmol/g), kidneys (54.4 nmol/g), and spleen (49.8 nmol/g). Identification and Quantitation of Metabolites:
A number of fractions (4 to 6) were isolated by preparative HPLC analysis of urine from rats treated with [14C]-EGPE. A component eluting at approximately 7 min under the preparative chromatographic conditions was presumed to be ethylene glycol (EG). The presence of this metabolite was confirmed by conversion to the dibenzoyl derivative followed by GC/MS quantitation. The acid, PAA, eluted at approximately 20 min and its structure was confirmed by extraction followed by GC/MS analysis. The glycine conjugate of PAA (N-propoxyscetyl glycine) eluted at approximately 29 min and its structure confirmed by conversion to the methyl ester followed by GC/MS analysis. In addition, components intermediate in retention times between that of the acid and the glycine conjugate were tentatively identified as the glucuronide and sulfate conjugates of EGPE by thermospray liquid chromatography/mass spectrometry.
Further characterization of urinary metabolites was obtained by chemical and enzymatic treatment of 12-hr, composite urine samples followed by analytical HPLC analysis. Treatment with P-glucuronidase resulted in the complete or nearly complete loss of a component having a retention time of 9.2 to 9.5 min. Comparable increases in levels of EGPE, seen following this β-glucuronidase treatment, confirmed the identity of this component as the glucuronic acid conjugate of EGPE. Treatment with arylsulfatase resulted in a consistent but small reduction in the amount of the glucuronic acid conjugate, presumably due to the presence of β-glucuronidase activity in the arylsulfatase. Thus, the presence of a sulfate conjugate based on sulfatase treatment could not be confirmed by enzymatic treatment. Treatment with 3 N HCl nearly eliminated the glycine conjugate peak (retention time of 9.8 to 10.6 min) with the production of a comparable amount of the acid, PAA. In addition, acid treatment caused the apparent loss of an unidentified component from some samples. This unknown component, present at levels as high as 3.2 % in buffer-treated samples, may be an acid-labile conjugate of either EGPE or PAA.
As many as 7 components were quantified by analytical HPLC analysis of 12-hr urine samples. The acid, PAA, accounted for the majority of the urinary radioactivity (41.6 % to 60.5 %) in these samples. The glycine conjugate accounted for 23.5 % to 37.6% of the radioactivity in urine samples. Lesser amounts of several other metabolites were also quantitated: ethylene glycol accounted for 6.0% to 14.4% of the radioactivity; EGPE –glucuronide accounted for 2.3% to 6.3% of the radioactivity; and EGPE itself was present at levels of 1.67 % to 4.55 % . The parent compound, EGPE, although detected was not consistently present in urine from all animals within any given dose group. In addition, two other unidentified components (Unknowns 1 and 2) were also present at levels of from 1.3 % to 5.0% of the urinary radioactivity.
HPLC analysis of 24-hr urine samples: The acid, PAA, and the glycine conjugate were detected in all samples and these accounted for the majority of radioactivity in the urine samples. A component eluting at the retention time of ethylene glycol was also observed in all urine samples except those from rats dosed orally at 150 mg/kg. Pharmacokinetic Analysis:
Following iv administration, the parent alcohol was rapidly removed from blood with a calculated first-order elimination rate constant (λel) of 5.57 hr-1 and corresponding half-life of 0.124 hr. The concentration of the acid, PAA, rose rapidly through a peak value at 0.5 hr of 21.5 µg/g (182 nmole/g) and was subsequently eliminated with a first-order rate constant of 0.924 hr-1, corresponding to a half-life in blood of 0.750 hr.
Similar to the results obtained in the iv study, a first-order elimination rate constant of 5.17 hr-1 and calculated half-life of 0.134 hr were obtained for EGPE following oral administration of 15 mg/kg. In addition, a rapid uptake phase was seen at this dose level with a calculated λel, of 24.73 hr-1. At the higher dose of 150 mg/kg, uptake and elimination of the parent alcohol was again rapid.
A single-compartment elimination rate constant for EGPE of 3.46 hr-1 was calculated, yielding an elimination half-life of 0.20 hr. The less rapid elimination at the higher oral dose level suggests more prolonged absorption or saturation of metabolism and/or elimination. In the case of the acid, PAA, formation and elimination kinetics following oral administration at 15 mg/kg were similar to those found in the iv study. Thus, the acid was eliminated with a first-order rate constant of 0.527 hr-1, corresponding to a half-life of the acid in blood of 1.32 hr. At the higher dose of 150 mg/kg, elimination of the acid appeared saturated. Analyzed concentrations of the acid reached 145 µg/g (1228 nmole/g) at the 2-hr sampling point. It was not possible to fit early (< 6 hr) blood concentrations of the acid in the 150 mg/kg oral study to an exponential uptake and elimination model. However, blood concentrations of the acid obtained following 6 hr were fitted to a single exponential function yielding an elimination rate constant of 0.293 hr-1 and corresponding half-life of 2.37 hr. This elevated half-life may represent saturation of metabolism or renal elimination of the acid.
Concentrations of the alcohol in blood increased during the 6-hr exposure reaching a peak level of 1.14 µg/g (10.9 nmole/g) at the 6-hr collection point. Following removal of excess test material at 6 hr, EGPE blood concentrations were too low to afford quantitation. PAA concentrations also rose steadily during the 6-hr exposure reaching a maximum level of 17.0 µg/g (144 nmole/g) at the 6-hr collection. Following the 6-hr exposure, blood concentrations of the acid declined with a first-order elimination rate constant of 0.45 hr-l, corresponding to a half-life of 1.54 hr.
In both studies, blood concentrations of the parent alcohol remained low but relatively constant over the duration of the 6-hr exposures. Curve-fitting analysis of EGPE concentrations during the exposures yielded steady-state (blood concentrations (Css) of 0.45 and 3.42 µg/g for the 25 and 175 ppm exposures, respectively. Following the cessation of exposure at 25 ppm, EGPE blood concentrations were too low to afford quantitation. Following the 6-hr exposure at 175 ppm, EGPE blood concentrations declined with a first order elimination rate constant of 5.20 hr-1, corresponding to a half-life of 0.133 hr. Concentrations of PAA increased steadily during the 6-hr exposures. The acid declined in concentration in blood subsequent to exposures with first-order rate constants for the elimination of 0.757 hr-1 and 0.479 hr-1 for the low and high concentrations, respectively. These values correspond to elimination half-lives of 0.92 and 1.45 hr, respectively.
Radioactivity in blood of rats dosed with [14C]-EGPE: The majority of 14C-activity is accounted for as EGPE and PAA prior to 2 hr. In later samples of blood, 14C-activity is present which cannot be accounted for as parent compound or acid metabolite. This residual blood activity presumably represents incorporation of label into normal metabolic intermediates, thus leading to complete metabolism to 14CO2. Activity in blood persisted through the end of the study. Similar results were obtained following oral, dermal, or inhalation exposures to [14C]-EGPE
Dermal Absorption Rate: A mean dermal absorption rate of 0.73 mg/cm2/hr was calculated based on recovered radioactivity from the dermal absorption and pharmacokinetics study. This yielded a value of 0.792 x 10-3cm/hr for the permeability coefficient (Kp)
Applicant's summary and conclusion
- Conclusions:
- In conclusion, EGPE is rapidly absorbed and excreted following either oral or inhalation exposure with a majority of administered dose eliminated within 12 h. Following administration of either 15 or 150 mg/kg [14C]-EGPE 97% and 96%, respectively, of the administered doses were recovered by 72 hr. The majority of activity eliminated (75 or 81 % respectively) was present in urine. Inhalation exposures at either 25 ppm or 175 ppm [14C]-EGPE resulted in similar patterns of elimination. The acid metabolite, 2-propoxyacetic acid (PAA), and its glycine conjugate, N-(2-propoxyacetyl)glycine, were the principle urinary metabolites identified regardless of route of administration. The relatively high amounts of residual radioactivity remaining in carcasses after 72 hr, as well as the appearance of significant amounts of radiolabeled CO2 suggests complete conversion of absorbed EGPE to components of intermediary metabolism. The similar absorption and elimination pharmacokinetics determined for EGPE and its metabolite, PAA, suggest that observed differences in the toxicities of EGPE and EGBE may be due to inherent differences in the acid metabolites. Glycine conjugation offers an additional, alternative elimination pathway in the rat and provides an explanation for the increased elimination rate observed for PAA versus that for BAA. This latter fact may contribute to a decreased toxicity of the acid metabolite observed in the rat. Only in the case of the 150 mg/kg oral dose of EGPE was elimination of the acid, PAA, apparently saturated. In this latter case, blood concentrations of the acid were in excess of 1200 nmole/g. Inhalation exposures at 175 ppm produced blood concentrations of the acid in excess of 600 nmole/g, but at this exposure level, elimination following the 6-hr exposures was linear. Thus, it is apparent that saturation of urinary elimination of the acid occur between 600 and 1200 nmole/g blood concentrations. Metabolite excretion patterns following dermal exposure are similar to those of oral and inhalation
- Executive summary:
The absorption, distribution, elimination, metabolism, and pharmacokinetics of ethylene glycol mono-n-propyl ether (EGPE) were determined following either intravenous, oral, dermal, or inhalation exposures of male Sprague-Dawley rats to 2-[ethylene-1,2-14C]-EGPE ([14C]-EGPE).
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