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EC number: 629-850-6 | CAS number: 1245638-61-2
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted according to standard guidelines in compliance with GLP.
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.19 (Estimation of the Adsorption Coefficient (KOC) on Soil and Sewage Sludge Using High Performance Liquid Chromatography (HPLC))
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: OECD 117 (Partition Coefficient (n-octanol/water), HPLC Method)
- Deviations:
- not specified
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC estimation method
- Media:
- other: HPLC column (acting as a soil/sewage sludge matrix)
- Test temperature:
- Not applicable
- Details on study design: HPLC method:
- EQUIPMENT
- Apparatus: HPLC
- Type: Alliance separation module 2695 (Waters, Milford, USA)
- Type, material and dimension of analytical (guard) column: Hypersil BDS-CN, 150 mm x 4.6 mm i.d., dp = 5 micrometer (Thermo, San Jose, USA)
- Detection system: Dual lambda absorbance detector 2487 (Waters)
MOBILE PHASES
- Type: 30/70 (v/v) methanol/water
- Experiments with additives carried out on separate columns: no
- Solutes for dissolving test and reference substances: 30/70 (v/v) methanol/water
REFERENCE SUBSTANCES
- Identity: thiourea (unretained compound), acetanilide, atrazine, monuron, 2,5-dichloroaniline, benzoic acid phenylester, fenthion, phenanthrene
DETERMINATION OF RETENTION TIMES
- Quantity of test substance introduced in the column: 10 microliter
- Quantity of reference substances: 10 microliter
REPETITIONS
- Number of determinations: duplicates
EVALUATION
- Calculation of capacity factors k': k' = (tr-t0)/t0 (tr = retention time; t0 = mean column dead time)
- Calibration curve: log k' = a log koc + b (a = slope; b = intercept) - Key result
- Type:
- other: log Koc (major constituent)
- Value:
- 1.81 dimensionless
- Remarks on result:
- other: PETIA
- Key result
- Type:
- other: log Koc (major constituent)
- Value:
- 2.64 dimensionless
- Remarks on result:
- other: PETRA
- Key result
- Type:
- other: log Koc (for all constituents)
- Value:
- ca. 0.45 - <= 3.73 dimensionless
- Remarks on result:
- other: log Koc range based on values for identified peaks
- Details on results (HPLC method):
- - Retention times of reference substances used for calibration: thiourea (unretained): 2.03 min; acetanilide 2.73 min; atrazine: 3.98 min; monuron: 3.76-3.78 min; 2,5 dichloroaniline: 4.54-4.56 min; benzoic acid phenylester: 8.13-8.21 min; Fenthion: 16.27-16.49 min; Phenanthrene: 16.08-16.22 min
- Details of fitted regression line (log k' vs. log Koc): log k' = 0.490 x log koc - 1.00 (r = 0.957, n = 14)
- Average retention data for test substance: PETIA; 3.572; PETRA: 5.983 - Validity criteria fulfilled:
- yes
- Conclusions:
- Under the conditions of the study, the log Koc of the test substance ranged from <0.45 and <=3.73. Therefore, following a conservative approach, the highest log Koc of 3.73 has been taken forward as the key value for the risk assessment.
- Executive summary:
A study was conducted to determine the log Koc of the test substance using the HPLC method. The test substance contains mainly pentaerythritol triacrylate (PETIA) and pentaerythritol tetraacrylate (PETRA) 32.9 % and 43.3 % of the total peak area respectively. Under the study conditions, the log Koc of PETIA was 1.81 and Koc of PETRA was 2.64. For the minor components, log Koc values are in between <0.45 and 3.73. Less than 10 % of the total peak area exceeded log Koc of 3 (Oudhoff, 2010a). Following a conservative approach, the highest log Koc of 3.73 has been taken forward as the key value for the risk assessment.
Reference
Koc of the test substance
|
Log Koc |
Area % |
Component 1 |
<0.45 |
0.3 |
Component 2 |
<0.45 |
1.3 |
Component 3 |
0.45 |
0.4 |
Component 4 |
0.84 |
5.6 |
Component 5 |
1.19 |
0.8 |
Component 6 |
1.51 |
0.2 |
Component 7 |
1.63 |
0.1 |
Component 8 (PETIA) |
1.81 |
32.9 |
Component 9 |
2.07 |
2.9 |
Component 10 |
2.36 |
0.3 |
Component 11 (PETRA) |
2.64 |
43.3 |
Component 12 |
2.74 |
1.3 |
Component 13 |
2.88 |
3.6 |
Component 14 |
3.13 |
0.2 |
Component 15 |
3.48 |
6.1 |
Component 16 |
3.73 |
0.8 |
Description of key information
Key value for chemical safety assessment
- Koc at 20 °C:
- 5 370
Additional information
A study was conducted to determine the log Koc of the test substance using the HPLC method. The test substance contains mainly pentaerythritol triacrylate (PETIA) and pentaerythritol tetraacrylate (PETRA) 32.9 % and 43.3 % of the total peak area respectively. Under the study conditions, the log Koc of PETIA was 1.81 and Koc of PETRA was 2.64. For the minor components, log Koc values are in between <0.45 and 3.73. Less than 10 % of the total peak area exceeded log Koc of 3 (Oudhoff, 2010a). Following a conservative approach, the highest log Koc of 3.73 (i.e., Koc = 5370) has been taken forward as the key value for the risk assessment.
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.
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