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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 813-338-6 | CAS number: 106155-02-6
- 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
Endpoint summary
Administrative data
Link to relevant study record(s)
- Endpoint:
- basic toxicokinetics, other
- Type of information:
- other: In accordance with REACH Annex VIII (8.8) an assessment of toxicokinetic behavior has been conducted to the extent that can be derived from the relevant available information.
- Adequacy of study:
- key study
- Study period:
- The assessment was conducted in March 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Relevant studies were reviewed by a qualified toxicologist with a view to fulfilling the requirements of Annex VIII (8.8).
- Objective of study:
- toxicokinetics
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- In accordance with REACH Annex VIII (8.8) an assessment of toxicokinetic behaviour has been conducted to the extent that can be derived from the relevant available information. The assessment is based on the Guidance on information requirements and chemical safety assessment R.7c: Endpoint specific guidance (ECHA, November 2014)
- GLP compliance:
- no
- Remarks:
- Not relevant for assessment
- Conclusions:
- The test item is a low molecular weight liquid that is fairly water soluble. Any oral ingestion of the test item may lead to absorption and systemic distribution, there may also be some limited adsorption via the dermal and inhalation routes. Changes in the liver indicate that the test item may be metabolised, but due to the water solubility, metabolism is probably not required for excretion via the kidney, which is the most likely route of excretion for test item.
- Executive summary:
The test item is a low molecular weight liquid that is fairly water soluble. Any oral ingestion of the test item may lead to absorption and systemic distribution, there may also be some limited adsorption via the dermal and inhalation routes. Changes in the liver indicate that the test item may be metabolised, but due to the water solubility, metabolism is probably not required for excretion via the kidney, which is the most likely route of excretion for test item.
- Endpoint:
- dermal absorption, other
- Remarks:
- in silico
- Type of information:
- calculation (if not (Q)SAR)
- Adequacy of study:
- supporting study
- Qualifier:
- no guideline followed
- Parameter:
- other: Absorption based on calculated Jmax
- Absorption:
- <= 40 %
- Conclusions:
- Calculated value Jmax = 6.659
Absorption ≤ 40% - Executive summary:
Calculated value Jmax = 6.659
Absorption ≤ 40%
Referenceopen allclose all
TOXICOKINETIC BEHAVIOUR
The substance is a liquid with a molecular weight of 194 mg/L.
The substance has a relatively low vapour pressure and is non-volatile and therefore inhalation is not considered to be a significant route of exposure.
The substance has a moderate log octanol/water partition coefficient (log Pow 4.1) and is relatively water soluble (59 mg/L).
There were moderate signs of toxicity in an acute oral toxicity study but no signs of toxicity in a dermal toxicity study.
A repeated dose toxicity study (on a read-across substance) showed some evidence of absorption.
The substance is a skin irritant.
A read-across substance was non-mutagenic and non-clastogenic in in-vitro genotoxicity studies, in either the presence or absence of an auxiliary metabolising system.
Absorption
The test item is a relatively low molecular weight liquid that is fairly soluble in water and has a moderate log Octanol: Water partition coefficient. This suggests that the test item has the potential to cross biological membranes, via diffusion, such as those of the gastro-intestinal tract following oral ingestion. The test item may also have some potential for uptake via micellular solubilisation. The results of the acute oral toxicity study showed moderate signs of systemic toxicity and mortality at a high dose (5000 mg/kg bodyweight). The repeated dose toxicity study (based on read across from (2E)-2-ethyl-4-(2,2,3-trimethyl-3-cyclopenten-1-yl)-buten-1-ol) shows signs of systemic toxicity (adverse effects) and 4 females treated at the highest dose (1000 mg/kg bw/day) were killed prior to scheduled termination for humane reasons related to effects of treatment with the test item. These results suggest that there is some absorption of the test item.
Some more limited passage across the dermal barrier may be possible as the substance is a liquid and the Log P value and water solubility favours low to moderate dermal absorption. Skin absorption was predicted to be ≤ 40% by a Skin Absorption Model (SAM), based on a calculated Jmax value. The substance is a skin irritant, and therefore damage to the skin surface may enhance penetration. The substance is not a skin sensitiser and the acute dermal toxicity study found no signs of systemic toxicity, suggesting dermal uptake is limited.
As the material does not exist as particulates and the material has low volatility (vapour pressure < 0.5kPa), exposure via the inhalation route is limited. The Log P value may be favourable for absorption directly across the respiratory tract epithelium by passive diffusion, and may also have some potential for uptake via micellular solubilisation. The systemic toxicity observed in oral toxicity studies that indicates the potential for absorption following ingestion, also indicates that the substance may also be absorbed if it is inhaled.
Distribution
As the test item is of low molecular weight and is water soluble, it can be assumed that any absorbed test item can be readily distributed in the water fraction of circulatory fluids.This may be supported by effects observed in the repeated dose toxicity study.
The lack of skin sensitization response would suggest the material does not bind to circulatory proteins.
The partition coefficient (Log Kow 4.082) may suggest that the test item has some limited potential to accumulate in body fat.
Metabolism
The results of the repeat dose toxicity study (based on read across from (2E)-2-ethyl-4-(2,2,3-trimethyl-3-cyclopenten-1-yl)-buten-1-ol) found bodyweight adjusted liver weights were higher than control in males and females after five weeks dosing at 300 or 1000 mg/kg/day. Enlarged livers were observed in females receiving 1000 mg/kg/day and centrilobular hepatocyte hypertrophy was seen in the liver of 2 females receiving 1000 mg/kg/day with enlarged livers. Biochemical changes were seen in females at 1000 mg/kg/day, such as increased levels of enzymes associated with liver function, cholesterol and bilirubin levels. This may suggest enhanced hepatic metabolism. However, the fact that the material is already fairly water soluble suggests that metabolism may not be required to enhance excretion.
Genotoxicity studiesin vitro(based on read across from 2-ethyl-4-(2,2,3-trimethyl-3-cyclopenten-1-yl)-2-buten-1-ol)show that the genotoxic potential of the test item is neither enhanced nor diminished in the presence of S9 microsomal metabolising system.
Excretion
Low molecular weight test items that are water soluble are most likely to be excreted via the kidney although the repeat dose toxicity/reproduction screening study gives no indication of route of excretion. Following oral ingestion, any test item that is not absorbed is likely to be excreted in the faeces
Calculated value Jmax = 6.659
Absorption ≤ 40%
Description of key information
The test item is a low molecular weight liquid that is fairly water soluble. Any oral ingestion of the test item may lead to absorption and systemic distribution, there may also be some limited adsorption via the dermal and inhalation routes. Changes in the liver indicate that the test item may be metabolised, but due to the water solubility, metabolism is probably not required for excretion via the kidney, which is the most likely route of excretion for test item.
Key value for chemical safety assessment
Additional information
TOXICOKINETIC BEHAVIOUR
The substance is a liquid with a molecular weight of 194 mg/L.
The substance has a relatively low vapour pressure and is non-volatile and therefore inhalation is not considered to be a significant route of exposure.
The substance has a moderate log octanol/water partition coefficient (log Pow 4.1) and is relatively water soluble (59 mg/L).
There were moderate signs of toxicity in an acute oral toxicity study but no signs of toxicity in a dermal toxicity study.
A repeated dose toxicity study (on a read-across substance) showed some evidence of absorption.
The substance is a skin irritant.
A read-across substance was non-mutagenic and non-clastogenic in in-vitro genotoxicity studies, in either the presence or absence of an auxiliary metabolising system.
Absorption
The test item is a relatively low molecular weight liquid that is fairly soluble in water and has a moderate log Octanol: Water partition coefficient. This suggests that the test item has the potential to cross biological membranes, via diffusion, such as those of the gastro-intestinal tract following oral ingestion. The test item may also have some potential for uptake via micellular solubilisation. The results of the acute oral toxicity study showed moderate signs of systemic toxicity and mortality at a high dose (5000 mg/kg bodyweight). The repeated dose toxicity study (based on read across from (2E)-2-ethyl-4-(2,2,3-trimethyl-3-cyclopenten-1-yl)-buten-1-ol) shows signs of systemic toxicity (adverse effects) and 4 females treated at the highest dose (1000 mg/kg bw/day) were killed prior to scheduled termination for humane reasons related to effects of treatment with the test item. These results suggest that there is some absorption of the test item.
Some more limited passage across the dermal barrier may be possible as the substance is a liquid and the Log P value and water solubility favours low to moderate dermal absorption. Skin absorption was predicted to be ≤ 40% by a Skin Absorption Model (SAM), based on a calculated Jmax value. The substance is a skin irritant, and therefore damage to the skin surface may enhance penetration. The substance is not a skin sensitiser and the acute dermal toxicity study found no signs of systemic toxicity, suggesting dermal uptake is limited.
As the material does not exist as particulates and the material has low volatility (vapour pressure < 0.5kPa), exposure via the inhalation route is limited. The Log P value may be favourable for absorption directly across the respiratory tract epithelium by passive diffusion, and may also have some potential for uptake via micellular solubilisation. The systemic toxicity observed in oral toxicity studies that indicates the potential for absorption following ingestion, also indicates that the substance may also be absorbed if it is inhaled.
Distribution
As the test item is of low molecular weight and is water soluble, it can be assumed that any absorbed test item can be readily distributed in the water fraction of circulatory fluids.This may be supported by effects observed in the repeated dose toxicity study.
The lack of skin sensitization response would suggest the material does not bind to circulatory proteins.
The partition coefficient (Log Kow 4.082) may suggest that the test item has some limited potential to accumulate in body fat.
Metabolism
The results of the repeat dose toxicity study (based on read across from (2E)-2-ethyl-4-(2,2,3-trimethyl-3-cyclopenten-1-yl)-buten-1-ol) found bodyweight adjusted liver weights were higher than control in males and females after five weeks dosing at 300 or 1000 mg/kg/day. Enlarged livers were observed in females receiving 1000 mg/kg/day and centrilobular hepatocyte hypertrophy was seen in the liver of 2 females receiving 1000 mg/kg/day with enlarged livers. Biochemical changes were seen in females at 1000 mg/kg/day, such as increased levels of enzymes associated with liver function, cholesterol and bilirubin levels. This may suggest enhanced hepatic metabolism. However, the fact that the material is already fairly water soluble suggests that metabolism may not be required to enhance excretion.
Genotoxicity studiesin vitro(based on read across from 2-ethyl-4-(2,2,3-trimethyl-3-cyclopenten-1-yl)-2-buten-1-ol)show that the genotoxic potential of the test item is neither enhanced nor diminished in the presence of S9 microsomal metabolising system.
Excretion
Low molecular weight test items that are water soluble are most likely to be excreted via the kidney although the repeat dose toxicity/reproduction screening study gives no indication of route of excretion. Following oral ingestion, any test item that is not absorbed is likely to be excreted in the faeces
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.