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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 306-115-5 | CAS number: 96152-43-1
- 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
Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 3.526 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 176.3 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- Good quality oral study available. While no inhalation exposure anticipated, it is possible to derive systemic NOAEC for this route using default assumptions and the oral data to extrapolate, as per ECHA guidance ("Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.)
- AF for dose response relationship:
- 1
- Justification:
- Adequate dosing and study information. No justification for deviating from the standard AF outlined in Ch R:8 based on the database.
- AF for differences in duration of exposure:
- 4
- Justification:
- 4 : in between sub-acute and sub-chronic (54 days) to chronic exposure
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- No allometric scaling for inhalation route
- AF for other interspecies differences:
- 2.5
- Justification:
- According to Chapter R.8-Dose [Concentration]-Response Regarding Human Health, an additional assessment factor of 2.5 should be applied for remaining differences between test species and human. In cases where differences are not related to basal metabolic rate, the assessment factor should be modified. In terms of dynamics, one might assume that animals and humans will respond in the same way (p. 33). Based on the physicochemical properties, absorption is believed to be limited to such a degree that metabolic differences are not relevant for remaining differences. for more details see systemic dermal DNELs.
- AF for intraspecies differences:
- 5
- Justification:
- Standard default value for workers as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for the quality of the whole database:
- 1
- Justification:
- Reliable study, good quality database
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 66.8 mg/m³
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 12.5
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 835 mg/m³
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- No allometric scaling for inhalation route
- AF for other interspecies differences:
- 2.5
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for intraspecies differences:
- 5
- Justification:
- Standard default value for workers as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 3.12 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 40
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 125 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- no route-to-route extrapolation needed
- AF for dose response relationship:
- 1
- Justification:
- No justification for deviating from the standard AF outlined in Ch R:8 based on the database.
- AF for differences in duration of exposure:
- 2
- Justification:
- It was considered relevant to include information from a 90d dietary feeding study (Haas 2010) on a related category material which demonstrated low systemic toxicity; it is considered that the properties of the registration material will mean that dermal absorption is very low and that bioavailability via the gut will be higher, thus tthis is a conservative application of oral data to enhance the database being used for this derivation. In short, the oral data can be used in a weight of evidence which provides for a more robust and longer term dataset - hence the AF for the duration of exposure can be reduced using this sub-chronic data.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for other interspecies differences:
- 1
- Justification:
- Justification for use of 1 for Remaining Differences: According to Chapter R.8-Dose [Concentration]-Response Regarding Human Health, an additional assessment factor of 2.5 should be applied for remaining differences between test species and human. In cases where differences are not related to basal metabolic rate, the assessment factor should be modified. In terms of dynamics, one might assume that animals and humans will respond in the same way. Based on the physicochemical properties, absorption is believed to be limited to such a degree that metabolic differences are not relevant for remaining differences. Physicochemical properties have a decisive influence on the penetration of molecules through the skin. EC# 272-234-3 has Log Kow 9.5, these parameters are not favourable for absorption when in contact with skin. This assumption was confirmed by a QSAR assay, which calculated dermal penetration coefficient (Kp) or Pd (the permeability of the skin) by using empirical formulas. This is supported by animal testing in which no effects were observed following acute dermal exposure and minimal effects were observed in subacute testing. These observations suggest poor percutaneous penetration and/or the substance has low inherent systemic toxicity. This adjustment is believed to apply for long term systemic effects via the dermal route for workers and general population, and also for the general population for acute toxicity (workers will wear PPE which will mean that only in consumers would the skin penetration element be a factor).
- AF for intraspecies differences:
- 5
- Justification:
- Standard default value for workers as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for the quality of the whole database:
- 1
- Justification:
- Reliable study used
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 80 mg/kg bw/day
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 4 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- No route to route extrapolation needed
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for other interspecies differences:
- 2.5
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health. Workers will wear PPE which will mean that dermal penetration potential is not a signficant factor in the toxicity, hence normal defaults apply.
- AF for intraspecies differences:
- 5
- Justification:
- Standard default value for workers as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- repeated dose toxicity
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
DNELS: Category approach and mammalian toxicity
The substance being Registered in this particular dossier is one of a series of chemically similar materials each of which is composed of a closely related series of alkylated phenol species. For further details on the Category, see section 13. The data for other members of the category can be used to complete the hazard characterisation for the Registration material where substance-specific data are lacking. For the derivation of DNEL values, the presence/absence of the highly refined base oil is taken into account here; the Registration material does not comprise as a constituent the base oil, but all toxicology testing has been carried out with oil present, hence the end results and DNELs are adjusted to take account of this and to end up with DNELs relevant to the active ingredient of this Registration material.
Summary of Toxicity (Registration material and category members)
The substance is not acutely toxic following oral and dermal routes of exposure. Inhalation exposure is unlikely to occur because the substance only exists in liquid form and it will not be aerosolised in its normal use pattern. The substance is not irritating either to the skin and eye and is not a sensitiser. It is not positive in any genotoxicity testing, and shows no potential for repeat dose toxicity or carcinogenicity based on existing data and expert judgement. There are some effects seen on fertility which are believed to be due to one component/impurity (the material is a UVCB) and hence classification for that one endpoint is performed using the % of that CMR material in the Registration substance (see Section 1 for composition details, Section 2 for Classification details).
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.87 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 100
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 86.96 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- Good quality oral study available. While no inhalation exposure anticipated, it is possible to derive systemic NOAEC for this route using default assumptions and the oral data to extrapolate, as per ECHA guidance ("Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.)
- AF for differences in duration of exposure:
- 4
- Justification:
- In between subacute and subchronic to chronic exposure
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- No allometric scaling applied via inhalation route
- AF for other interspecies differences:
- 2.5
- Justification:
- Standard default value after route to route extrapolation as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health."
- AF for intraspecies differences:
- 10
- Justification:
- Standard default value for the general population as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for the quality of the whole database:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 66.8 mg/m³
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 12.5
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 835 mg/m³
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- No allometric scaling via inhalation
- AF for other interspecies differences:
- 2.5
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health."
- AF for intraspecies differences:
- 10
- Justification:
- Standard default value for general population as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health."
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.56 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 80
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 125 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- no extrapolation needed
- AF for differences in duration of exposure:
- 2
- Justification:
- It was considered relevant to include information from a 90d dietary feeding study on a related category material which demonstrated low systemic toxicity; it is considered that the properties of the registration material will mean that dermal absorption is very low and that bioavailability via the gut will be higher, thus tthis is a conservative application of oral data to enhance the database being used for this derivation. In short, the oral data can be used in a weight of evidence which provides for a more robust and longer term dataset - hence the AF for the duration of exposure can be reduced using this sub-chronic data.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for other interspecies differences:
- 1
- Justification:
- According to Chapter R.8-Dose [Concentration]-Response Regarding Human Health, an additional assessment factor of 2.5 should be applied for remaining differences between test species and human. In cases where differences are not related to basal metabolic rate, the assessment factor should be modified. In terms of dynamics, one might assume that animals and humans will respond in the same way (p. 33). Based on the physicochemical properties, absorption is believed to be limited to such a degree that metabolic differences are not relevant for remaining differences. Physicochemical properties have a decisive influence on the penetration of molecules through the skin. EC# 272-234-3 has Log Kow 9.5, these parameters are not favourable for absorption when in contact with skin. This assumption was confirmed by a QSAR assay, which calculated dermal penetration coefficient (Kp) or Pd (the permeability of the skin) by using empirical formulas. This is supported by animal testing in which no effects were observed following acute dermal exposure and minimal effects were observed in subacute testing. These observations suggest poor percutaneous penetration and/or the substance has low inherent systemic toxicity. This adjustment is believed to apply for long term systemic effects via the dermal route for workers and general population, and also for the general population for acute dermal toxicity (where no PPE are worn).
- AF for intraspecies differences:
- 10
- Justification:
- Standard default value for the general population as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for the quality of the whole database:
- 1
- Justification:
- adequate database and study
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 40 mg/kg bw/day
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 100
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 4 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- No extrapolation required
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for other interspecies differences:
- 2.5
- Justification:
- Standard default value for the general population as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for intraspecies differences:
- 10
- Justification:
- Standard default value for the general population as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- repeated dose toxicity
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.25 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 400
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 100 mg/kg bw/day
- AF for differences in duration of exposure:
- 4
- Justification:
- from inbetween subacute and subchronic to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for other interspecies differences:
- 2.5
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for intraspecies differences:
- 10
- Justification:
- Standard default value for the general population as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for the quality of the whole database:
- 1
- Justification:
- Reliable study
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 25 mg/kg bw/day
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 100
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 2 500 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- no extrapolation required
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for other interspecies differences:
- 2.5
- Justification:
- Standard default value as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for intraspecies differences:
- 10
- Justification:
- Standard default value for general population as indicated by the ECHA guidance document “Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health.
- AF for the quality of the whole database:
- 1
- Justification:
- Good quality study and supporting information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
see above Discussion section (workers) for toxicity summary and category rationale.
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.