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EC number: 202-114-8 | CAS number: 91-99-6
- 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
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- November 27th, 2012 - April 7th, 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.7 (Degradation: Abiotic Degradation: Hydrolysis as a Function of pH)
- Version / remarks:
- (2008)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Version / remarks:
- (2004)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 835.2120 (Hydrolysis of Parent and Degradates as a Function of pH at 25°C)
- Version / remarks:
- (2008)
- Deviations:
- no
- GLP compliance:
- yes
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- Samples for analysis were taken immediately after preparation (t=0) and after 5 days. The samples taken at t=5 days were cooled to room temperature using running tap water.
- Buffers:
- Acetate buffer pH 4, 0.01 M: solution of 16.7% 0.01 M sodium acetate in water and 83.3% 0.01 M acetic acid in water. The buffer contains 0.0009% (w/v) sodium azide.
Phosphate buffer pH 7, 0.01 M: solution of 0.01 M potassium di-hydrogenphosphate in water adjusted to pH 7 using 1 N sodium hydroxide. The buffer contains 0.0009% (w/v) sodium azide.
Borate buffer pH 9, 0.01 M: solution of 0.01 M boric acid in water and 0.01 M potassium chloride in water adjusted to pH 9 using 1 N sodium hydroxide. The buffer contains 0.0009% (w/v) sodium azide. - Details on test conditions:
- Performance of the study:
The rate of hydrolysis of the test substance as a function of pH was determined at pH values normally found in the environment (pH 4-9).
Preliminary test - Tier 1:
The test substance was spiked to the buffer solutions at a target concentration of 20 mg/L using a spiking solution in water. Each solution was filter-sterilised through a 0.2 µm FP 30/0.2 CA-S filter (Whatman, Dassel, Germany) and transferred into a sterile vessel. To exclude oxygen, nitrogen gas was purged through the solution for 5 minutes. For each sampling time, duplicate sterile vessels under vacuum were filled with 6 ml test solution and placed in the dark in a temperature controlled environment at 49.9°C +/- 0.1°C.
The concentration of the test substance in the test samples was determined immediately after preparation (t=0) and after 5 days. The samples taken at t=5 days were cooled to room temperature using running tap water. The samples were diluted with buffer solution to obtain a concentration within the calibration range.
Blank buffer solutions containing a similar content of blank spiking solution were treated similarly as the test samples and analysed at t=0.
The pH of each of the test solutions (except for the blanks) was determined at each sampling time. - Number of replicates:
- Two
- Positive controls:
- no
- Negative controls:
- no
- Preliminary study:
- At pH 4, 7 and pH 9, < 10% of hydrolysis was observed after 5 day (half-life time at 25°C is > 1 year). According to the guideline, no further tests were required.
- Test performance:
- RECOVERIES
- Recovery is the concentration analysed at t=0 relative to the nominal concentration.
- Mean recovery in the table below is the mean of duplicate test samples.
- The mean recoveries of all the buffer solutions fell within he acceptable range of 90-110%; the analytical method was adequate to support the hydrolysis study on the test substance. - Transformation products:
- not measured
- % Recovery:
- 100
- pH:
- 4
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- other: actual recovery: 107%
- % Recovery:
- 100
- pH:
- 7
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- other: actual recovery: 102%
- % Recovery:
- 100
- pH:
- 9
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- other: actual recovery: 101%
- Key result
- Remarks on result:
- other: hydrolytically stable based on preliminary test (at pH 4, 7 and 9)
- Details on results:
- The analytical results of the preliminary test are given in the table hereunder.
At pH 4, pH 7 and pH 9 a degree of hydrolysis of < 10% was observed after 5 days. It demonstrated that the half-life time of the test substance at 25°C is > 1 year. According to the guideline, no further tests were required.
No test substance was detected in the blank buffer solutions.
The mean recoveries of the buffer solutions fell within the criterion range of 90-110%. It demonstrated that the analytical method was adequate to support the hydrolysis study on the test substance. - Validity criteria fulfilled:
- yes
- Conclusions:
- A hydrolysis study was carried out according to EC C.7, OECD 111, EPA OPPTS 830.2120 and GLP. At pH 4, 7 and 9 and 50 °C, a degree of < 10% of hydrolysis was observed after 5 days. This corresponds with a half-life time at 25°C of > 1 year; the substance can be considered hydrolytically stable at pH 4, 7 and 9.
- Endpoint:
- hydrolysis
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: read-across from a structural analogue
- Justification for type of information:
- 1. HYPOTHESIS FOR THE ANALOGUE APPROACH
The substance Accelerator (Reaction mass of 2,2'-[(4-methylphenyl)imino]bisethanol and 2-[[2-(2-hydroxyethoxy)ethyl](4-methylphenyl)amino]-ethanol)) is a structural analogue of 2,2'-[(3-methylphenyl)imino]bisethanol. Accelerator contains ca. 50-60% of 2,2'-[(4-methylphenyl)imino]bisethanol as the main constituent. The only difference between 2,2'-[(4-methylphenyl)imino]bisethanol and the target chemical 2,2'-[(3-methylphenyl)imino]bisethanol is the position of the methyl group in the phenyl ring (para vs meta with regard to the imino group). This is not expected to have any significant influnce on either physico-chemical properties or toxicological behavior of the substances. Next to 2,2'-[(4-methylphenyl)imino]bisethanol Accelerator contains ca. 35-45% of 2-{[2-(2-hydroxyethoxy)ethyl](4-methylphenyl)amino}ethanol, which contains the same structural moiety of 2,2'-[(4-methylphenyl)imino]bisethanol, but with one alcohol moiety transformed into the ester bond with ethylene glycol. As Accelerator contains over 50% of the structural analogue of 2,2'-[(3-methylphenyl)imino]bisethanol, with the only difference being the position of the methyl group in the phenyl ring, it is considered acceptable to read across the results of the hydrolysis study from Accelerator to 2,2'-[(3-methylphenyl)imino]bisethanol. Furthermore, a structural analogue of 2-{[2-(2-hydroxyethoxy)ethyl](4-methylphenyl)amino}ethanol, 2-{[2-(2-hydroxyethoxy)ethyl](3-methylphenyl)amino}ethanol, differing only by the position of the methyl group in the phenyl ring (meta vs. para) is also present as an impurity up to 7% concentration in the target chemical 2,2'-[(3-methylphenyl)imino]bisethanol.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
The source chemical is the Reaction mass of 2,2'-[(4-methylphenyl)imino]bisethanol and 2-[[2-(2-hydroxyethoxy)ethyl](4-methylphenyl)amino]-ethanol)), containing ca. 50-60% of 2,2'-[(4-methylphenyl)imino]bisethanol, ca. 35-45% of 2-{[2-(2-hydroxyethoxy)ethyl](4-methylphenyl)amino}ethanol and ca. 2-4% of 2-[{2-[2-(2-hydroxyethoxy)ethoxy]ethyl}(4-methylphenyl)amino]ethanol. The purity of the substance is ca. 90-100%.
The target chemical is 2,2'-[(3-methylphenyl)imino]bisethanol with the purity of 90-100%. The substance contains up to 7% 2-{[2-(2-hydroxyethoxy)ethyl](3-methylphenyl)amino}ethanol as an impurity.
3. ANALOGUE APPROACH JUSTIFICATION
The substance Accelerator (Reaction mass of 2,2'-[(4-methylphenyl)imino]bisethanol and 2-[[2-(2-hydroxyethoxy)ethyl](4-methylphenyl)amino]-ethanol)) is a structural analogue of 2,2'-[(3-methylphenyl)imino]bisethanol. Accelerator contains ca. 50-60% of 2,2'-[(4-methylphenyl)imino]bisethanol as the main constituent. The only difference between 2,2'-[(4-methylphenyl)imino]bisethanol and the target chemical 2,2'-[(3-methylphenyl)imino]bisethanol is the position of the methyl group in the phenyl ring (para vs meta with regard to the imino group). This is not expected to have influnce on hydrolytical behavior of the substances. Next to 2,2'-[(4-methylphenyl)imino]bisethanol Accelerator contains ca. 35-45% of 2-{[2-(2-hydroxyethoxy)ethyl](4-methylphenyl)amino}ethanol, which contains the same structural moiety of 2,2'-[(4-methylphenyl)imino]bisethanol, but with one alcohol moiety transformed into the ester bond with ethylene glycol. The presence of the ester moiety is not expected to influence the hydrolytical stability of the substances. As Accelerator contains over 50% of the structural analogue of 2,2'-[(3-methylphenyl)imino]bisethanol, with the only difference being the position of the methyl group in the phenyl ring, it is considered acceptable to read across the results of the hydrolysis study from Accelerator to 2,2'-[(3-methylphenyl)imino]bisethanol. Furthermore, a structural analogue of 2-{[2-(2-hydroxyethoxy)ethyl](4-methylphenyl)amino}ethanol, 2-{[2-(2-hydroxyethoxy)ethyl](3-methylphenyl)amino}ethanol, differing only by the position of the methyl group in the phenyl ring (meta vs. para) is also present as an impurity up to 7% concentration in the target chemical 2,2'-[(3-methylphenyl)imino]bisethanol.
Furthermore, the data matrix constructed based on the available physico-chemical and (eco)toxicological properties of both substances indicates that the substances have comparable properties across the complete range of endpoints.
Based on this, read-across from Accelerator to 2,2'-[(3-methylphenyl)imino]bisethanol is considered to be justified.
4. DATA MATRIX
Accelerator 2,2'-[(3-methylphenyl)imino]bisethanol
Molecular weight ~217 195.26
State of the substance at ambient conditions Clear slightly yellowish to brown viscous liquid Colourless solidified melt
Melting/freezing point [ºC] Not determined (glass transition temp. of -28ºC) 66.9
Boiling point [ºC] - (decomposition of test item at >275ºC) - (reaction and/or decomposition of the test item at > 225°C)
Relative density at 20 ºC 1.11 1.115
Vapour pressure at 25 ºC [Pa] 0.0025 0.000223 (calculated)
Surface tension [mN/m] 65.2, not surface active 65.4 at 1 g/L, not surface active
Water solubility at 20 ºC [mg/L] 21800 9330
Partition coefficient n-octanol/water [log Pow] 2.17 1.9
Flash point [ºC] 176 193
Flammability Not flammable, not pyrophoric Not flammable, not pyrophoric
Explosive properties Not explosive Not explosive
Auto-ignition temperature 395ºC 395ºC
Oxidising properties Not oxidizing Not oxidizing
Viscosity (dynamic, mPas) 2797 5474
Ready biodegradability Not readily biodegradable Not readily biodegradable
Hydrolysis as function of pH Half life for hydrolysis >1 y at 25 ºC, hydrolytically stable Read-across
Adsorption/desorption [log Koc] 2.33 (weight-averaged of 4 main components) Read-across
Acute toxicity to daphnia, EC50 [mg/L] 48 107 mg/L
Growth inhibition algae, EC50, NOEC [mg/L] >100; 100 >100; 100
Acute toxicity to fish, LC50 [mg/L] >100 >102
Acute oral, LD50 [mg/kg bw] 619 300-2000
Skin irritation/corrosion Skin irritant cat 2. Read-across
Eye irritation/corrosion Corrosive, cat 1. Read-across
Skin sensitisation Sensitiser Read-across
In vitro gene mutation in bacteria (Ames test) Mutagenic Non-mutagenic
In vitro cytogenicity in mammalian cells Not clastogenic, does not disturb mitotic processes Not clastogenic, does not disturb mitotic processes
In vivo genotox (Comet) Not mutagenic No data
28-day repeated dose toxicity NOAEL 100 mg/kg bw LOAEL 50 mg/kg bw/day - Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.7 (Degradation: Abiotic Degradation: Hydrolysis as a Function of pH)
- Version / remarks:
- (2008)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Version / remarks:
- (2004)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 835.2120 (Hydrolysis of Parent and Degradates as a Function of pH at 25°C)
- Version / remarks:
- (2008)
- Deviations:
- no
- Preliminary study:
- At pH 4, 7 and pH 9, < 10% of hydrolysis was observed after 5 day (half-life time at 25°C is > 1 year). According to the guideline, no further tests were required.
- Test performance:
- RECOVERIES
- Recovery is the concentration analysed at t=0 relative to the nominal concentration.
- Mean recovery in the table below is the mean of duplicate test samples.
- The mean recoveries of all the buffer solutions fell within he acceptable range of 90-110%; the analytical method was adequate to support the hydrolysis study on the test substance. - Transformation products:
- not measured
- % Recovery:
- 100
- pH:
- 4
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- other: actual recovery: 107%
- % Recovery:
- 100
- pH:
- 7
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- other: actual recovery: 102%
- % Recovery:
- 100
- pH:
- 9
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- other: actual recovery: 101%
- Key result
- Remarks on result:
- other: hydrolytically stable based on preliminary test (at pH 4, 7 and 9)
- Details on results:
- The analytical results of the preliminary test are given in the table hereunder.
At pH 4, pH 7 and pH 9 a degree of hydrolysis of < 10% was observed after 5 days. It demonstrated that the half-life time of the test substance at 25°C is > 1 year. According to the guideline, no further tests were required.
No test substance was detected in the blank buffer solutions.
The mean recoveries of the buffer solutions fell within the criterion range of 90-110%. It demonstrated that the analytical method was adequate to support the hydrolysis study on the test substance. - Validity criteria fulfilled:
- yes
- Conclusions:
- A hydrolysis study with a structural analogue of 2,2'-[(3-methylphenyl)imino]bisethanol, Accelerator, was carried out according to EC C.7, OECD 111, EPA OPPTS 830.2120 and GLP. At pH 4, 7 and 9 and 50 °C, a degree of < 10% of hydrolysis was observed after 5 days. This corresponds with a half-life time at 25°C of > 1 year; thus the substance can be considered hydrolytically stable at pH 4, 7 and 9. This result can be read across to 2,2'-[(3-methylphenyl)imino]bisethanol.
- Executive summary:
A hydrolysis study with a structural analogue of 2,2'-[(3-methylphenyl)imino]bisethanol, Accelerator, was carried out according to EC C.7, OECD 111, EPA OPPTS 830.2120 and GLP. At pH 4, 7 and 9 and 50 °C, a degree of < 10% of hydrolysis was observed after 5 days. This corresponds with a half-life time at 25°C of > 1 year; thus the substance can be considered hydrolytically stable at pH 4, 7 and 9. According to the guideline, no further tests were required. The mean recoveries of the buffer solutions fell within the criterion range of 90-110%. It demonstrated that the analytical method was adequate to support the hydrolysis study on the test substance.
This result can be read across to 2,2'-[(3-methylphenyl)imino]bisethanol.
Referenceopen allclose all
Table. Preliminary test - hydrolysis of the substance at pH 4, pH 7 and pH 9 at 50.0 ±1 °C:
pH code |
Sampling time |
Analysed concentration |
Degree of hydrolysis |
Actual pH |
|
Individual |
Mean |
||||
|
|
|
|
|
|
pH 4 |
0 hours |
21.6 |
|
|
4.1 |
|
|
21.4 |
|
|
4.1 |
|
|
|
|
|
|
|
5 days |
20.9 |
2.8 |
3.3 |
4.1 |
|
|
20.7 |
3.8 |
|
4.1 |
|
|
|
|
|
|
pH 7 |
0 hours |
20.5 |
|
|
7.0 |
|
|
20.5 |
|
|
7.1 |
|
|
|
|
|
|
|
5 days |
19.4 |
5.1 |
4.7 |
7.0 |
|
|
19.6 |
4.3 |
|
7.0 |
|
|
|
|
|
|
pH 9 |
0 hours |
20.1 |
|
|
9.0 |
|
|
20.1 |
|
|
9.0 |
|
|
|
|
|
|
|
5 days |
19.5 |
3.0 |
2.9 |
9.0 |
|
|
19.6 |
2.8 |
|
9.0 |
|
|
|
|
|
|
Table. Preliminary test - hydrolysis of the substance at pH 4, pH 7 and pH 9 at 50.0 ±1 °C:
pH code |
Sampling time |
Analysed concentration |
Degree of hydrolysis |
Actual pH |
|
Individual |
Mean |
||||
|
|
|
|
|
|
pH 4 |
0 hours |
21.6 |
|
|
4.1 |
|
|
21.4 |
|
|
4.1 |
|
|
|
|
|
|
|
5 days |
20.9 |
2.8 |
3.3 |
4.1 |
|
|
20.7 |
3.8 |
|
4.1 |
|
|
|
|
|
|
pH 7 |
0 hours |
20.5 |
|
|
7.0 |
|
|
20.5 |
|
|
7.1 |
|
|
|
|
|
|
|
5 days |
19.4 |
5.1 |
4.7 |
7.0 |
|
|
19.6 |
4.3 |
|
7.0 |
|
|
|
|
|
|
pH 9 |
0 hours |
20.1 |
|
|
9.0 |
|
|
20.1 |
|
|
9.0 |
|
|
|
|
|
|
|
5 days |
19.5 |
3.0 |
2.9 |
9.0 |
|
|
19.6 |
2.8 |
|
9.0 |
|
|
|
|
|
|
Description of key information
In a Tier 1 study (in accordance with EC C.7, OECD 111, EPA OPPTS 830.2120), performed with a structural analogue of 2,2’-[(3-methylphenyl)imino]bisethanol, Accelerator, < 10% of hydrolysis was observed at pH 4, 7 and 9 after 5 days at 50 °C. Therefore the half-life time at 25°C is > 1 year and the substance can be considered hydrolytically stable at pH 4, 7 and 9. This result can be read across to 2,2’-[(3-methylphenyl)imino]bisethanol.
Key value for chemical safety assessment
Additional information
No hydrolysis study with 2,2’-[(3 -methylphenyl)imino]bisethanol is available; however, adequate data are available on its structural analogue Accelerator (Reaction mass of 2,2’-[(4-methylphenyl)imino]bisethanol and 2-[[2-(2-hydroxyethoxy)ethyl](4-methylphenyl)amino]-ethanol). Based on structural similarities of the substances and their similar physico-chemical and (eco)toxicological properties, read-across from Accelerator to 2,2’-[(3-methylphenyl)imino]bisethanol is considered to be justified.
The hydrolysis study with the structural analogue of 2,2’-[(3-methylphenyl)imino]bisethanol, Accelerator, was carried out according to EC C.7, OECD 111, EPA OPPTS 830.2120 and GLP. At pH 4, 7 and 9 and 50 °C, a degree of < 10% of hydrolysis was observed after 5 days. This corresponds with a half-life time at 25°C of > 1 year; thus the substance can be considered hydrolytically stable at pH 4, 7 and 9. According to the guideline, no further tests were required. The mean recoveries of the buffer solutions fell within the criterion range of 90-110%. It demonstrated that the analytical method was adequate to support the hydrolysis study on the test substance.
This result can be read across to 2,2’-[(3-methylphenyl)imino]bisethanol.
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.