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Diss Factsheets
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EC number: 439-730-3 | CAS number: -
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics, other
- Remarks:
- expert statement
- Type of information:
- other: expert statement
- Adequacy of study:
- key study
- Study period:
- 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Expert statement, no study available
Data source
Reference
- Reference Type:
- other company data
- Title:
- Unnamed
- Year:
- 2 019
- Report date:
- 2007
Materials and methods
- Objective of study:
- toxicokinetics
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: ECHA Guidance R .7c
- Version / remarks:
- 2017
- Principles of method if other than guideline:
- Expert statement
- GLP compliance:
- no
Test material
- Reference substance name:
- (trans(trans))-4'-vinyl-4-(4-methylphenyl)bicyclohexyl
- EC Number:
- 439-730-3
- EC Name:
- (trans(trans))-4'-vinyl-4-(4-methylphenyl)bicyclohexyl
- Cas Number:
- 155041-85-3
- Molecular formula:
- Hill formula: C21H30 CAS formula: C21H30
- IUPAC Name:
- (1r,1'r,4r,4'r)-4-ethenyl-4'-(4-methylphenyl)-1,1'-bi(cyclohexane)
Constituent 1
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Oral route
Bioavailability via oral route is strongly linked to physico-chemical properties of the substance (ECHA Guidance, 2017). Generally, oral absorption is favored for molecular weights below 500 g/mol and with a logPow in the range of -1 to 4. Thus, with a logPow greater than 8.6 the substance would be expected to not passively pass biological membranes. In addition, the substance is highly insoluble in water. However, micellular formation in the gastrointestinal tract (GIT) could enable absorption processes. Moreover, the molecular weight of the substances is well below 500 g/mol and could thus contribute to a favored absorption. In addition, the substance is not expected to undergo hydrolysis based on its chemical structure. Abiotic degradation is thus not relevant for the oral route of exposure. Taken together, the physico-chemical properties of the substance indicate that intestinal absorption cannot be completely ruled out.
The above considerations are confirmed by findings of toxicity studies with the test substance.
In an acute oral toxicity study with rats no mortality or other signs of toxicity were observed up to the limit dose of 2000 mg/kg bw.
However, a 28-day repeated dose toxicity study as well as a Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test revealed clear effects following oral administration at dose levels of above 15 mg/kg bw/d, including mortality at doses of 1000 mg/kg bw/d for up to 6 days. Based on the observed findings the test item is classified for specific target organ toxicity after repeated exposure (STOT RE) Cat. 2 (adrenal glands). Therefore, there is clear indication that the test item and/or its metabolites become systemically available via the oral route.
Dermal route
Regarding dermal exposure, the substance is considered to unlikely permeate the skin. According to ECHA guidance on toxicokinetics, there are no exclusion criteria for skin permeability, but a molecular weight of > 500 Da and a log Pow of > 4 are given as indicators for low absorption (10% or less). Considering the molecular weight, the test item would not be critical, however, its logPow of approx. 8.6 will probably not favor dermal permeation. Further, based on accepted calculation models and an expert statement provided in IUCLID Section 7.1.2 (reference 7.2.1-1), no or only very small amounts are expected to become systemically available upon dermal exposure. The above considerations are in line with findings of an acute dermal toxicity study in rats (reference 7.2.3-1). No signs of toxicity were observed up to the limit dose of 2000 mg/kg bw. Moreover, it is noted that the test item is not classified for local effects such as skin or eye irritation and no skin sensitisation was observed in vivo (references 7.3.1-1, 7.3.2-1 and 7.4.1-1). Taken together, this indicates that the test item will not readily penetrate skin layers.
Inhalation route
Due to a very low vapor pressure of 1.9E-4 Pa it is very unlikely that the substance becomes available as a vapor and the boiling point of the substance was determined to be 190 °C at 1013 hPa. The substance is a solid of very low dustiness. Therefore, exposure via inhalation is considered not relevant for the substance. However, in the unlikely case of inhalation, the substance would be expected to pass biological membranes taking into account same considerations as for the oral route. - Details on distribution in tissues:
- As mentioned above, no or very poor bioavailability is expected for the test item via the dermal route, whereas absorption upon ingestion is considered to be likely based on physicochemical properties and as confirmed by in vivo toxicity studies. Repeated dose toxicity studies revealed specific effects in target organs adrenal glands, indicating that either the substance itself or one of its metabolites reached this tissue following oral administration. Based on its low water solubility and high logPow value the test item is expected to be absorbed by micellular formation and as such taken up and transported via the lymph system, similar to other lipophilic constituents of the diet. Further, protein binding is expected rather than dissolution in the plasma in terms of distribution via the blood stream.
Based on its low water solubility and high logPow value, bioaccumulating potential cannot completely be ruled out for the test item. However, based on a experimental study in fish, a steady state BCF mean value of 163 was determined, confirming that the test item is of no concern in regards to bioaccumulation (reference 5.3.1-1).
- Details on excretion:
- The based on its low water solubility test item is not expected to be eliminated via the urine unless it undergoes metabolic transformation increasing its hydrophilicity. Elimination via the bile would thus be more likely.
Metabolite characterisation studies
- Details on metabolites:
- There is no experimental data available regarding potential metabolism of the test item.
Considering its chemical structure oxidation of the double bound of the aromatic ring or the vinyl group by phase I enzymes such as CYP 450 can be anticipated and will predominantly occur in the liver. Further, conjugation reactions by phase II enzymes such as glutathione-S-transferase in order to increase water solubility and thus facilitate excretion might occur. Nascent (cyclo-) alcohol groups might further represent a substrate for Alcohol as well as Aldehyde dehydrogenases.
Metabolism of the test item in the liver can be assumed, because the liver was found to be a target organ in both repeated dose toxicity studies as a result of metabolic adaptation (reference 7.5.1-1 and 7.5.1-2). Because of the reversibility of the observed effects (e.g. on liver), the substance is most likely eliminated from the organism. Based on results of in vitro tests where experiments were conducted with as well as without exogenous metabolic activation it can be stated that adding rat liver S9 did not lead to an increased (cyto-) toxicity in any of the tests (reference 7.6.1-1 and 7.6.1-2). Therefore, activation of toxicity by metabolic transformation is considered unlikely to occur in the organism.
Applicant's summary and conclusion
- Conclusions:
- Based on the physicochemical properties, particularly water solubility, logPow and molecular weight, absorption via the gastrointestinal tract is possible for the test substance, whereas uptake following dermal exposure is less relevant. Based on its very low vapor pressure it is highly unlikely that the test substance will become systemically available after inhalation. Abiotic transformation e.g. hydrolysis is not expected. If absorbed, the test item would be distributed by binding to plasma protein due to its low water solubility and be eliminated via bile or the urine following metabolic transformation. Bioaccumulation is excluded based on experimental data.
- Executive summary:
Toxicokinetic analysis of the test item
There are no experimental studies available on toxicokinetics of the test item. Therefore its toxicokinetic properties are assessed based on its physico-chemical properties as well as from data available from toxicity studies and in accordance with ECHA Guidance R .7c (2017).
The test substance is a crystalline white solid at room temperature and of low dustiness. The test item, being a mono-constituent substance, has a molecular weight of 282.47 g/mol and a relative density of 1.04. Its melting point was determined to be 66 °C and whereas the boiling point is at 190 °C at 1013 hPa. The substance is considered highly insoluble in water, as water solubility was found to be smaller than 0.005 mg/L. Partition coefficient (logPow) of the substance was estimated to be 8.6 being the highest calibration standard of the method applied. Vapor pressure of the substance was determined to be 1.95E-4 Pa at 25 °C.
1.1 Absorption
Oral route
Bioavailability via oral route is strongly linked to physico-chemical properties of the substance (ECHA Guidance, 2017). Generally, oral absorption is favored for molecular weights below 500 g/mol and with a logPow in the range of -1 to 4. Thus, with a logPow greater than 8.6 the substance would be expected to not passively pass biological membranes. In addition, the substance is highly insoluble in water. However, micellular formation in the gastrointestinal tract (GIT) could enable absorption processes. Moreover, the molecular weight of the substances is well below 500 g/mol and could thus contribute to a favored absorption.
In addition, the substance is not expected to undergo hydrolysis based on its chemical structure. Abiotic degradation is thus not relevant for the oral route of exposure.
Taken together, the physico-chemical properties of the substance indicate that intestinal absorption cannot be completely ruled out.The above considerations are confirmed by findings of toxicity studies with the test substance. In an acute oral toxicity study with rats no mortality or other signs of toxicity were observed up to the limit dose of 2000 mg/kg bw.
However, a 28-day repeated dose toxicity study as well as a Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test revealed clear effects following oral administration at dose levels of above 15 mg/kg bw/d, including mortality at doses of 1000 mg/kg bw/d for up to 6 days. Based on the observed findings the test item is classified for specific target organ toxicity after repeated exposure (STOT RE) Cat. 2 (adrenal glands). Therefore, there is clear indication that the test item and/or its metabolites become systemically available via the oral route.
Dermal route
Regarding dermal exposure, the substance is considered to unlikely permeate the skin. According to ECHA guidance on toxicokinetics, there are no exclusion criteria for skin permeability, but a molecular weight of > 500 Da and a log Pow of > 4 are given as indicators for low absorption (10% or less). Considering the molecular weight, the test item would not be critical, however, its logPow of approx. 8.6 will probably not favor dermal permeation. Further, based on accepted calculation models and an expert statement provided in IUCLID Section 7.1.2 (reference 7.2.1-1), no or only very small amounts are expected to become systemically available upon dermal exposure.
The above considerations are in line with findings of an acute dermal toxicity study in rats (reference 7.2.3-1). No signs of toxicity were observed up to the limit dose of 2000 mg/kg bw. Moreover, it is noted that the test item is not classified for local effects such as skin or eye irritation and no skin sensitisation was observed in vivo (references 7.3.1-1, 7.3.2-1 and 7.4.1-1). Taken together, this indicates that the test item will not readily penetrate skin layers.
Inhalation route
Due to a very low vapor pressure of 1.9E-4 Pa it is very unlikely that the substance becomes available as a vapor and the boiling point of the substance was determined to be 190 °C at 1013 hPa. The substance is a solid of very low dustiness. Therefore, exposure via inhalation is considered not relevant for the substance. However, in the unlikely case of inhalation, the substance would be expected to pass biological membranes taking into account same considerations as for the oral route.
1.3 Distribution
As mentioned above, no or very poor bioavailability is expected for the test item via the dermal route, whereas absorption upon ingestion is considered to be likely based on physicochemical properties and as confirmed by in vivo toxicity studies. Repeated dose toxicity studies revealed specific effects in target organs adrenal glands, indicating that either the substance itself or one of its metabolites reached this tissue following oral administration. Based on its low water solubility and high logPow value the test item is expected to be absorbed by micellular formation and as such taken up and transported via the lymph system, similar to other lipophilic constituents of the diet. Further, protein binding is expected rather than dissolution in the plasma in terms of distribution via the blood stream.
Based on its low water solubility and high logPow value, bioaccumulating potential cannot completely be ruled out for the test item. However, based on a experimental study in fish, a steady state BCF mean value of 163 was determined, confirming that the test item is of no concern in regards to bioaccumulation (reference 5.3.1-1).
1.4 Metabolism
There is no experimental data available regarding potential metabolism of the test item.
Considering its chemical structure oxidation of the double bound of the aromatic ring or the vinyl group by phase I enzymes such as CYP 450 can be anticipated and will predominantly occur in the liver. Further, conjugation reactions by phase II enzymes such as glutathione-S-transferase in order to increase water solubility and thus facilitate excretion might occur. Nascent (cyclo-) alcohol groups might further represent a substrate for Alcohol as well as Aldehyde dehydrogenases.
Metabolism of the test item in the liver can be assumed, because the liver was found to be a target organ in both repeated dose toxicity studies as a result of metabolic adaptation (reference 7.5.1-1 and 7.5.1-2). Because of the reversibility of the observed effects (e.g. on liver), the substance is most likely eliminated from the organism.
Based on results of in vitro tests where experiments were conducted with as well as without exogenous metabolic activation it can be stated that adding rat liver S9 did not lead to an increased (cyto-) toxicity in any of the tests (reference 7.6.1-1 and 7.6.1-2). Therefore, activation of toxicity by metabolic transformation is considered unlikely to occur in the organism.
1.5 Elimination
The based on its low water solubility test item is not expected to be eliminated via the urine unless it undergoes metabolic transformation increasing its hydrophilicity. Elimination via the bile would thus be more likely.
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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