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EC number: 204-104-9 | CAS number: 115-77-5
- 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
Endpoint summary
Administrative data
Description of key information
No evidence of skin sensitisation potential was seen in a LLNA when tested upto 25%.
Key value for chemical safety assessment
Skin sensitisation
Link to relevant study records
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 31 July to 05 September 2015
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- July 2010
- Deviations:
- no
- GLP compliance:
- yes
- Type of study:
- mouse local lymph node assay (LLNA)
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): Pentaerythritol
- Physical state: crystalline solid
- Analytical purity: 98.8%
- Lot/batch No.: 4410102701
- Expiration date of the lot/batch: 18 December 2016
- Storage condition of test material: ambient temperature, protected from light - Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Charles River UK Limited, Margate, Kent, UK
- Age at study initiation: 8-11 weeks
- Weight at study initiation: 18-22 g
- Housing: All mice were housed in pairs in solid-bottomed polycarbonate/polypropylene cages with a stainless steel grid top and an integrated food hopper. The control animals were housed remotely from the test animals. Sterilised white wood shavings were used as bedding. Cardboard play tunnels, nesting material and wooden chewsticks were placed in each cage as environmental enrichment.
- Diet: SDS Rat and Mouse (modified) No. 1 Diet SQC Expanded, ad libitum
- Water: water from the public supply, ad libitum
- Acclimation period: at least 8 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 18-21°C (target 19-23°C)
- Humidity (%): 49-74% (40-70%)
- Air changes (per hr): at least 10/hour
- Photoperiod (hrs dark / hrs light): 12 hour cycle
IN-LIFE DATES: From: 12 August 2015 To: 21 August 2015 - Vehicle:
- acetone/olive oil (4:1 v/v)
- Concentration:
- Preliminary test: 25%
Main test: 0, 5, 10, 25% - No. of animals per dose:
- Preliminary test: 2
Main test: 4 - Details on study design:
- Preliminary test: a preliminary test was conducted with 2 females, to investigate the toxicity/irritancy potential of the test material. The animals received an open application of 25 μL of the test item formulation onto the dorsum of each ear once daily for 3 consecutive days (Days 1 to 3). Animals were checked for viability early in the morning and again as late as possible on each day, and were examined daily for reaction to treatment. The body weight of each individual animal was recorded on Day 1 (before the first dose) and on Day 6. On Day 1 (predose) and Days 3 and 6 the thickness of both ears of each mouse was measured using digital callipers. In addition, both ears were observed for erythema and the scores recorded. Excessive local skin irritation is indicated by an erythema score ≥3 and/or increase in ear thickness of ≥25% on any day of measurement. A dose concentration giving rise to excessive local skin irritation is not suitable for administration on the main study. Animals were euthanised on Day 6. There were no signs of systemic toxicity, no clear effects on body weight, and no local irritation noted. The appropriate dose concentrations were selected for administration in the main study on the basis of these findings. Concentrations were taken from the concentration series detailed in the regulatory guidelines (OECD 429).
Main test: The concentrations selected from the main test were 0, 5, 10 and 25%. Animals received an open application of 25 μL of the appropriate formulation onto the dorsum of each ear on 3 consecutive days (Days 1 to 3). There was no treatment on Days 4 to 6. On Day 6 each animal received an intravenous injection (250 μL) of phosphate buffered saline (PBS) containing 21 μCi of [methyl-3H] thymidine into the lateral tail vein. Approximately 5 h after intravenous administration all animals were euthanised by exposure to a rising concentration of carbon dioxide and the major blood vessels were severed to exsanguinate. Each pair of draining auricular lymph nodes was collected from each animal, a visual inspection of the nodes was made, and the animal was then discarded. A single cell suspension of lymph node cells from each paired sample was prepared by gentle
disaggregation through a 200 μm mesh stainless steel gauze into conical centrifuge tubes. The lymph node cells were washed in an excess of PBS (approximately 1 mL) and the mesh was discarded. The lymph node cells were then centrifuged at approximately 1300 g for 10 min at 4°C. The supernatant was drawn off and the pellet was washed a second time with approximately 1 mL PBS and then centrifuged (also at approximately 1300 g for 10 min at 4°C). Following centrifugation, the supernatant was discarded and the pellet was precipitated with approximately 1 mL 5% trichloroacetic acid at 2-8°C overnight. The pellet was again centrifuged at approximately 1300 g for 10 min at 4°C and the supernatant discarded. The pellet was then re-suspended in 200 μL ‘Solvable’, an aqueous-based solubiliser and the suspension transferred to a vial containing 10 mL scintillation fluid (Aquasafe 500 plus liquid). Incorporation of tritiated thymidine was measured by β-scintillation counting and was expressed as disintegrations per minute (DPM).
Calculation of results: Results were corrected for background radiation and expressed as the Stimulation Index (SI). This was obtained by dividing the mean DPM obtained from each group by the mean DPM for the vehicle control group. The SI for the vehicle control group, therefore, is one. A positive response is indicated by an SI≥3, together with consideration of dose-response and, where appropriate, statistical significance. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- Group means and standard deviations were calculated for disintegrations per minute. Group means and standard deviations were calculated for body weights, along with body weight gains. The percentage of ear thickness of the preliminary test mice was calculated. Dixon’s Q-test (Dean and Dixon, 1951) for the detection of a single outlier was performed on disintegrations per minute values. No other formal statistical analyses were performed.
- Positive control results:
- The experimental phase of a study using hexylcinnamaldehyde (HCA) at concentrations of 5% and 25% was completed in February 2015. The results from this study (Charles River Study No. 992477) produced stiumulation indices for HCA, when compared with the control group, of 1.7 and
10.5, for 5% and 25%, respectively. This was considered to provide evidence that the methodology used at the Test Facility is valid. - Parameter:
- SI
- Value:
- 0.7
- Test group / Remarks:
- 5% test item
- Parameter:
- SI
- Value:
- 1
- Test group / Remarks:
- 10% test item
- Parameter:
- SI
- Value:
- 0.9
- Test group / Remarks:
- 25% test item
- Parameter:
- other: disintegrations per minute (DPM)
- Value:
- 2 874
- Test group / Remarks:
- 0% - vehicle control
- Parameter:
- other: disintegrations per minute (DPM)
- Value:
- 1 935
- Test group / Remarks:
- 5% test item
- Parameter:
- other: disintegrations per minute (DPM)
- Value:
- 2 733
- Test group / Remarks:
- 10% test item
- Parameter:
- other: disintegrations per minute (DPM)
- Value:
- 2 580
- Test group / Remarks:
- 25% test item
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- Under the conditions of the study, since treatment with Pentaerythritol at concentrations of up to 25% did not achieve a stimulation index of ≥3, it was considered that the test item does not have the potential to cause skin irritation, and classification is not required.
- Executive summary:
The delayed contact hypersensitivity potential of pentaerythritol was determined in a local lymph node assay (LLNA) according to OECD 429. The study was performed using female CBA/Ca mice. A formulation trial established that a 25% (250 mg/mL) concentration in acetone:olive oil (4:1 v/v) (AOO) was the maximum practicable concentration. A preliminary test was conducted by administering a 25% concentration of pentaerythritol to a group comprising 2 mice. As a result of the findings from the preliminary test, the following formulation concentrations were selected for the main study: 0, 5, 10 and 25%. The vehicle control group received AOO only. Treatment was for 3 consecutive days. Three days after the final application each animal received an intravenous injection of [methyl-³H] thymidine into the lateral tail vein. Approximately 5 hours later the draining lymph nodes were collected in order that incorporation of tritiated thymidine could be assessed by scintillation counting. There were no signs of systemic toxicity, and no signs of local irritation. The stimulation indices (SI) for 5%, 10% and 25%, when compared with the control group, were 0.7, 1.0 and 0.9, respectively. Under the conditions of the study, since treatment with pentaerythritol at concentrations of up to 25% did not achieve a stimulation index of ≥3, it was considered that the test item does not have the potential to cause skin irritation. Pentaerythritol does not meet the criteria for classification as a skin sensitiser according to Regulation (EC) No 1272/2008.
Reference
Preliminary test: there were no signs of systemic toxicity, no clear effects on body weight, and no local irritation noted.
Therefore, a 25% concentration of Pentaerythritol was selected as the highest concentration for the main study.
Main test: there were no systemic signs and no signs of local irritation in any animal during the observation period. Body weight gains were considered to be acceptable for mice of this age and strain.
Dixon’s Q-test for the detection of a single outlier was performed on the disintegrations per minute (DPM) data. Applying 95% confidence limits for a population of 4, none of the DPM values were found to be outliers.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
No evidence of skin sensitisation potential was seen in a modern, GLP and OECD429 guideline compliant LLNA performed with pentaerythritol (Robertson, 2015). There are no known reports of worker exposure to pentaerythritol resulting in allergic reactions. It is concluded that pentaerythritol is not a skin sensitiser.
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Additional information:
No study is available; no method has been validated for the investigation of respiratory sensitisation. There are no known reports of worker exposure resulting in allergic asthma.
Justification for classification or non-classification
There is no evidence that pentaerythritol is a skin sensitiser or respiratory sensitiser. No classification is proposed for skin sensitisation on the basis on a negative LLNA conducted with pentaerythritol. There are no known reports of worker exposure resulting in allergic dermatitis or asthma. No classification for sensitisation is required according to Regulation (EC) No 1272/2008.
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