Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 203-227-5 | CAS number: 104-68-7
- 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:
- 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- This study was conducted as a part of the range finding study to the Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test (OECD TG 422 and US EPA OPPTS 870.3650) 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:
- 2 012
Materials and methods
- Objective of study:
- toxicokinetics
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Deviations:
- no
- Principles of method if other than guideline:
- not applicable
- GLP compliance:
- yes
Test material
- Reference substance name:
- 2-(2-phenoxyethoxy)ethanol
- EC Number:
- 203-227-5
- EC Name:
- 2-(2-phenoxyethoxy)ethanol
- Cas Number:
- 104-68-7
- Molecular formula:
- C10H14O3
- IUPAC Name:
- 2-(2-phenoxyethoxy)ethan-1-ol
- Test material form:
- other: liquid
- Details on test material:
- - Name of test material (as cited in study report): Diethylene Glycol Mono Phenyl Ether
- Physical state: liquid
- Analytical purity: 99.92%
- Impurities (identity and concentrations): no information available
- Composition of test material, percentage of components: The purity of the test material was determined to be 99.92%, after correcting for water, by gas chromatography with identification by proton nuclear magnetic resonance and gas chromatography mass spectrometry.
- Lot/batch No.: Lot # 201103261-7-18
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- other: Crl:CD (SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River (Portage, Michigan)
- Age at study initiation: approximately 8 weeks at initiation of treatment
- Weight at study initiation:
- Fasting period before study: not applicable
- Housing: housed singly in solid stainless steel cages
- Diet (ad libitum): Animals were provided LabDiet Certified Rodent Diet #5002 (PMI Nutrition International, St. Louis, Missouri) in meal form.
- Water: Municipal water was provided ad libitum
- Acclimation period: Animals were acclimated to the laboratory for at least one week prior to the start of the study
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22°C with a tolerance of ± 1°C (and a maximum permissible excursion of ± 3°C)
- Humidity (%): 40-70%
- Air changes (per hr): 10-15 times/hour (average)
- Photoperiod (hrs dark / hrs light): 12-hour light/dark (on at 6:00 a.m. and off at 6:00 p.m.)
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- DIET PREPARATION
- Rate of preparation of diet (frequency): Diets were prepared by serially diluting a concentrated test material-feed mixture (premix) with ground feed. Premixes were prepared periodically throughout the study based on stability data. Diets were prepared weekly for two weeks prior to breeding of the P1 adults. Initial concentrations of test material in the diet were calculated from historical body weights and feed consumption data. Subsequently, the concentrates of the test material in the diets were calculated from the most recent body weight and feed consumption data. To avoid potential overdosing during the breeding period, co-housed animals were provided with the female diet, which was of lower concentration. Following breeding, the male diet was prepared weekly until necropsy. During gestation and lactation, females from each dose group were provided with the appropriate dietary concentration of diethylene glycol mono phenyl ether given during breeding. - Duration and frequency of treatment / exposure:
- Animals were dosed daily via the diet for the duration of the rangefinding study; 14 days.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
250, 500 and 1000 mg/kg diet
- No. of animals per sex per dose / concentration:
- 5 male + 5 female rats/dose
- Control animals:
- yes, plain diet
- Positive control reference chemical:
- not applicable
- Details on study design:
- - Dose selection rationale: The exposure levels were chosen on the basis of previous toxicity data, limited to an acute oral LD50 of 3526 mg/kg in rats with the objective of estimating a maximum tolerated dose.
- Rationale for animal assignment: random - Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: urine and blood, plasma
- Time and frequency of sampling: Urine samples were obtained from all surviving rats/sex/group on day 13 and blood samples were collected on day 14 at 6:30 a.m., 1:30 p.m and 3:30 p.m. ((± 30 minutes).
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine and blood plasma
- Time and frequency of sampling: Urine samples were obtained from all surviving rats/sex/group on day 13 and blood samples were collected on day 14 at 6:30 a.m., 1:30 p.m and 3:30 p.m. ((± 30 minutes).
- From how many animals: (samples pooled or not): all animals
- Method type(s) for identification: LC-MS (urine) and HPLC-ESI-MS-MS (blood)
- Limits of detection and quantification: Refer to attachments
- Test Material Name: 2-(2-Phenoxyethoxy)acetic acid
Vendor: Ryan Scientific, Inc.
Lot#: R446803
Molecular Formula: C10H12O4
Molecular Weight: 196.2
Purity: NA
Test Material Name: Phenoxyacetic acid
CAS Number: 122-59-8
Vendor: Acros Organics
Lot#: A0282821
Molecular Formula: C8H8O3
Molecular Weight: 152.2
Purity: 99.4% (Reference: Van den Broek, 2012)
Internal Standards
Chemical Name: 13C2-2-(Phenoxyethoxy) acetic acid
Vendor: Chemalong Laboratories, LLC
Lot #: CA207503
This internal standard was used to facilitate quantitation of PEAA during mass spectral analysis.
Chemical Name: D5-Phenoxyacetic acid
Vendor: C/D/N Isotopes Inc.
Lot #: E57P2
This internal standard was used to facilitate quantitation of PAA during mass spectral analysis.
Chemical Name: D5-Diethylene Glycol Phenyl Ether
Vendor: Chemalong Laboratories, LLC
Lot #: CA204402
This internal standard was not used to facilitate quantitation of DiEPH during mass spectral analysis but is included in this report for future assays.
Standard Preparation:
A mixed stock solution was prepared at 10239 µg DiEPH, 10160 µg PEAA and 10101 µg PAA / mL acetonitrile. This mixed stock solution was further diluted with acetonitrile to prepare standards with concentrations between 0.0101 and 10.1 µg/mL. A 100-µL aliquot of mixed internal standard solution (D5-DiEPH at 10.0 µg/mL, D5-PAA at 10.0 µg/mL and 13C2-PEAA at 20.0 µg/mL) was added to each standard for a final volume of 1.0 mL.
Plasma Sample Preparation:
The following was added or performed:
- 20 µL of plasma was added to a micro-centrifuge tube
- 20 µL of acetonitrile
- Briefly vortex-mix samples
- Centrifuge samples at 15,000 rcf for 10 minutes
- 10 µL of supernatant was placed into a limited-volume autosampler vial
- 10 µL of internal standard solution (D5-DiEPH at 10.0 µg/mL, D5-PAA at 10.0 µg/mL and 13C2-PEAA at 20.0 µg/mL) was added
- 80 µL of Milli-Q Water
- Briefly vortex-mix samples
- Samples were analyzed by HPLC/ESI/MS/MS
Fortified Plasma Sample (Spike) Preparation:
The following was added or performed:
- 100 µL of plasma was added to a micro-centrifuge tube
- 100 µL of acetonitrile was added containing DiEPH, PEAA and PAA to achieve plasma concentrations of 0.5, 5 and 50 µg analyte / mL blood.
- Briefly vortex-mix samples
- Centrifuge samples at 15,000 rcf for 10 minutes
- 10 µL of supernatant was placed into a limited-volume autosampler vial
- 10 µL of internal standard solution (D5-DiEPH at 10.0 µg/mL, D5-PAA at 10.0 µg/mL and 13C2-PEAA at 20.0 µg/mL) was added
- 80 µL of Milli-Q Water
- Briefly vortex-mix samples
- Samples were analyzed by HPLC/ESI/MS/MS
Urine Sample Preparation:
The following was added or performed:
- 1000 µL of urine sample was placed in a 1-dram glass vial
- 100 µL of concentrated hydrochloric acid (HCl) was added
- Briefly vortex-mix samples
- Heat samples overnight at 80 °C
- Centrifuge samples at 3400 rpm for 10 minutes
- 100 µL of supernatant was placed into a clean 1-dram glass vial
- 900 µL of Milli-Q Water was added to the vial
- Briefly vortex-mix samples
- The diluted supernatant was further diluted with Milli-Q water to bring the sample in range for analysis (target concentrations between 0.01 – 10 µg/mL)
- 100 µL of internal standard solution (D5-DiEPH at 10.0 µg/mL, D5-PAA at 10.0 µg/mL and 13C2-PEAA at 20.0 µg/mL) was added, the final volume of each sample was 1.0 mL.
- Briefly vortex-mix samples
- Samples were analyzed by HPLC/ESI/MS/MS
Fortified Urine Sample (Spike) Preparation:
The following was added or performed:
- 900 µL of control urine sample was placed in a 1-dram glass vial
- 100 µL of Milli-Q water was added containing DiEPH, PEAA and PAA to achieve urine concentrations of 1, 10, 100 and 1000 µg analyte / mL urine
- 100 µL of concentrated hydrochloric acid (HCl) was added
- Briefly vortex-mix samples
- Heat samples overnight at 80 °C
- Centrifuge samples at 3400 rpm for 10 minutes
- 100 µL of supernatant was placed into a clean 1-dram glass vial
- 900 µL of Milli-Q Water was added to the vial
- Briefly vortex-mix samples
- The diluted supernatant was further diluted with Milli-Q water to bring the sample in range for analysis (target concentrations between 0.01 – 10 µg/mL).
- 100 µL of internal standard solution (D5-DiEPH at 10.0 µg/mL, D5-PAA at 10.0 µg/mL and 13C2-PEAA at 20.0 µg/mL) was added, the final volume of each sample was 1.0 mL.
- Briefly vortex-mix samples
- Samples were analyzed by HPLC/ESI/MS/MS
Analysis Conditions for Sample Analyser:
Pump: Agilent 1200 Series; G1312B
Autosampler: Agilent 1200 Series; G1367C
Column Heater: Agilent 1200 Series; G1316B
Mass Spectrometer: Agilent Triple Quad; G6410A
Analytical Column:Phenomenex Kintex Phenyl-Hexyl, 2.1 x 100 mm, 1.7 µm
Guard Column: None
HPLC Eluent - A = Milli Q water + 0.1% formic acid
B = Acetonitrile + 0.1% formic acid
Gradient:
Time (min) Flow Rate (mL/min) % A % B
0 0.400 98 2
0.5 0.400 98 2
8 0.400 60 40
9 0.400 0 100
10 0.400 0 100
10.5 0.400 98 2
14 0.400 98 2
Injection Volume: 5 µL
Column Temp: 35 °C
Source: ESI
Mode: MRM
Analyte Q1 Mass (amu) Q3 Mass (amu) Dwell (ms) Polarity CE (V)
PEAA 197 121 200 Positive 10
13C2-PEAA 199 121 200 Positive 10
DiEPH 183 121 200 Positive 6
D5-DiEPH* 188 121 200 Positive 6
PAA 151 93 200 Negative 10
D5-PAA 156 98 200 Negative 10
* This transition was collected but not used
Fragmentor:75 V
Dry Gas Heater: 350 °C
Dry Gas Flow: 12 L/min
Nebulizer Pressure: 30 psi
Sheath Gas Temp: 400 °C
Sheath Gas Flow: 12 L/min
Capillary Voltage:4000 V - Statistics:
- Standard statistical methods were employed
Results and discussion
- Preliminary studies:
- not applicable
Main ADME results
- Type:
- metabolism
- Results:
- The relevant biomarkers were identified as (DiEPH), 2-(2-Phenoxyethoxy) acetic acid (PEAA) and Phenoxyacetic acid (PAA).
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- not applicable
- Details on distribution in tissues:
- not applicable
- Details on excretion:
- not applicable
Toxicokinetic parametersopen allclose all
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 1st: Blood plasma: Half-life values based on 2-(2-Phenoxyethoxy) acetic acid (PEAA) blood levels were approximately 7.4 hours, on average, and ranged 3.9-15.6 hours
- Test no.:
- #2
- Toxicokinetic parameters:
- half-life 1st: Blood plasma: As Phenoxyacetic acid (PAA) was present in 50 per cent of the blood samples, systemic exposure (AUC24h) and elimination half-life (t½) values could not be calculated.
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- Qualitative Metabolic Biomarker Identification - A series of analytical screening experiments were conducted to determine the relevant biomarkers in rat plasma and urine following dietary administration of DiEPh at dose levels of 0, 250, 500, or 1000 mg/kg/day. The proposed metabolic scheme of DiEPh presented in the attachment Figure 1 which shows the likely metabolic pathways and related biomarkers that were screened. These target analytes included: ethylene glycol (EG), diethylene glycol (DEG), phenoxy ethanol (PE), phenol, hydroxylethoxy acetic acid (HEAA), diglycolic acid (DGA), glycolic acid (GA), and oxalic acid (OA), diethylene glycol mono phenyl ether (DiEPh), phenoxyethoxy acetic (PEAA), and phenoxy acetic acid (PAA). These screening experiments identified the relevant biomarkers as DiEPh, PEAA, and PAA. The levels of the other potential biomarkers were low relative to both background PEAA or PAA levels. Therefore, no definitive quantitative data was generated for EG, DEG, PE, HEAA, DGA, GA, or OA.
Quantitative Toxicokinetic Assessment - DiEPh was not present at levels above the lower limit of quantitation (LLQ) in most of the blood samples. The two metabolites, PEAA and PAA, were present at higher levels in the blood. PEAA was present well above the limit of quantitation and in nearly all of the blood samples from exposed animals, while PAA was present in 50 percent of the blood samples For this reason, systemic exposure (AUC24h) and elimination half-life (t½) values could only be calculated for PEAA. PEAA systemic exposure (AUC24h) values were dose-proportional in both males and females. Half-life values based on PEAA blood levels were approximately 7.4 hours, on average, and ranged 3.9-15.6 hours.
DiEPh, PEAA, and PAA all were present at concentrations above the LLQ in all urine samples from treated animals. On average, only 1.3 percent of the dose was excreted as DiEPh in the 24 hour urine, whereas 39.3 percent of the dose was excreted as PEAA and 4.3 percent of the dose was excreted as PAA. Urine levels of all three analytes were dose-proportional. These data suggest DiEPh was rapidly metabolized at all dose levels. A major portion of the dose was metabolized to PEAA (≥ 39.3% of the administered dose, 87.5% of the recovered dose). A smaller portion was metabolized to PAA (≥ 4.3% of the administered dose, 9.6% of the recovered dose). There was no apparent saturation of absorption, distribution or elimination at any dose level. Thus, DiEPh exhibits linear kinetics up to, and including, 1000 mg/kg/day
Bioaccessibility (or Bioavailability)
- Bioaccessibility (or Bioavailability) testing results:
- no information available
Any other information on results incl. tables
None
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
Under the conditions of the study, there was no apparent saturation of absorption, distribution or elimination at any dose level and DiEPh exhibits linear kinetics up to, and including, 1000 mg/kg/day. DiEPh was rapidly metabolized at all dose levels with the major metabolites detected PEAA (≥ 39.3% of the administered dose) and PAA (≥ 4.3% of the administered dose). 50% of PEAA was present in blood samples with half-life average values of approximately 7.4 hours. - Executive summary:
Selected rat plasma and urine samples were screened for the relevant biomarkers following dietary consumption of rodent feed prepared to deliver diethylene glycol mono phenyl ether DiEPH doses of 0, 250, 500 and 1000 mg/kg/day. The relevant biomarkers were identified as (DiEPH), 2-(2-Phenoxyethoxy) acetic acid (PEAA) and Phenoxyacetic acid (PAA). Plasma and urine (following acid hydrolysis) samples were analyzed for these biomarkers by high performance liquid chromatography (HPLC), negative/positive ion electrospray ionization (-/+ESI), with mass spectrometry detection operating in multiple reaction ion monitoring (MRM) mode. PAA and PEAA were quantified using stable isotope internal standard calibration and diethylene glycol phenyl ether was analyzed using external standard calibration.
Qualitative Metabolic Biomarker Identification - A series of analytical screening experiments were conducted to determine the relevant biomarkers in rat plasma and urine following dietary administration of DiEPh at dose levels of 0, 250, 500, or 1000 mg/kg/day. The proposed metabolic scheme of DiEPh presented in the attachment Figure 1 which shows the likely metabolic pathways and related biomarkers that were screened. These target analytes included: ethylene glycol (EG), diethylene glycol (DEG), phenoxy ethanol (PE), phenol, hydroxylethoxy acetic acid (HEAA), diglycolic acid (DGA), glycolic acid (GA), and oxalic acid (OA), diethylene glycol mono phenyl ether (DiEPh), phenoxyethoxy acetic (PEAA), and phenoxy acetic acid (PAA). These screening experiments identified the relevant biomarkers as DiEPh, PEAA, and PAA. The levels of the other potential biomarkers were low relative to both background PEAA or PAA levels. Therefore, no definitive quantitative data was generated for EG, DEG, PE, HEAA, DGA, GA, or OA.
Quantitative Toxicokinetic Assessment - DiEPh was not present at levels above the lower limit of quantitation (LLQ) in most of the blood samples. The two metabolites, PEAA and PAA, were present at higher levels in the blood. PEAA was present well above the limit of quantitation and in nearly all of the blood samples from exposed animals, while PAA was present in 50 percent of the blood samples For this reason, systemic exposure (AUC24h) and elimination half-life (t½) values could only be calculated for PEAA. PEAA systemic exposure (AUC24h) values were dose-proportional in both males and females. Half-life values based on PEAA blood levels were approximately 7.4 hours, on average, and ranged 3.9-15.6 hours.
DiEPh, PEAA, and PAA all were present at concentrations above the LLQ in all urine samples from treated animals. On average, only 1.3 percent of the dose was excreted as DiEPh in the 24 hour urine, whereas 39.3 percent of the dose was excreted as PEAA and 4.3 percent of the dose was excreted as PAA. Urine levels of all three analytes were dose-proportional. These data suggest DiEPh was rapidly metabolized at all dose levels. A major portion of the dose was metabolized to PEAA (≥ 39.3% of the administered dose, 87.5% of the recovered dose). A smaller portion was metabolized to PAA (≥ 4.3% of the administered dose, 9.6% of the recovered dose). There was no apparent saturation of absorption, distribution or elimination at any dose level. Thus, DiEPh exhibits linear kinetics up to, and including, 1000 mg/kg/day.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.