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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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
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EC number: 307-301-9 | CAS number: 97593-01-6
- 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
Bioaccumulation: aquatic / sediment
Administrative data
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: TGD guideline, QSAR calculation, acceptable with restrictions
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in Section 13.
Cross-reference
- Reason / purpose for cross-reference:
- read-across: supporting information
Reference
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: TGD guideline, QSAR calculation, acceptable with restrictions
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Principles of method if other than guideline:
- This model uses a parabolic relationship between log Kow and BCF to predict the BCF of a test substance. This parabolic relationship applies to substances with a log Kow >6.
- GLP compliance:
- no
- Remarks:
- not applicable
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not applicable - Details on sampling:
- not applicable
- Vehicle:
- no
- Details on preparation of test solutions, spiked fish food or sediment:
- not applicable
- Test organisms (species):
- Pimephales promelas
- Details on test organisms:
- not applicable
- Route of exposure:
- aqueous
- Test type:
- not specified
- Water / sediment media type:
- natural water: freshwater
- Hardness:
- not applicable
- Test temperature:
- not applicable
- pH:
- not applicable
- Dissolved oxygen:
- not applicable
- TOC:
- not applicable
- Salinity:
- not applicable
- Details on test conditions:
- not applicable
- Nominal and measured concentrations:
- not applicable
- Details on estimation of bioconcentration:
- not applicable
- Type:
- other: log BCF
- Value:
- 4.37 dimensionless
- Basis:
- not specified
- Remarks on result:
- other: based on a log Kow 8.06
- Details on kinetic parameters:
- not applicable
- Metabolites:
- not applicable
- Results with reference substance (positive control):
- not applicable
- Details on results:
- not applicable
- Reported statistics:
- not applicable
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The calculated log BCF is 4.37.
- Executive summary:
An experimental BCF is not available for 1 -hexadecene. In the absence of measured data the use of a QSAR to predict the BCF is an appropriate technique to use. The use of the parabolic bioconcentration factor for aquatic organisms QSAR recommended in the Technical Guidance Document (2003) is appropriate for 1 -hexadecene as its log Kow falls within the applicability domain of the model.
Data source
Reference
- Reference Type:
- publication
- Title:
- Use of polynomial expressions to describe the bioconcentration of hydrophobic chemicals by fish.
- Author:
- Connell and Hawker
- Year:
- 1 988
- Bibliographic source:
- Ecotoxicol. Environ. Saf. 16, 242-257.
Materials and methods
- Principles of method if other than guideline:
- This model uses a parabolic relationship between log Kow and BCF to predict the BCF of a test substance. This parabolic relationship applies to substances with a log Kow >6.
- GLP compliance:
- no
- Remarks:
- not applicable
Test material
- Reference substance name:
- Hexadec-1-ene
- EC Number:
- 211-105-8
- EC Name:
- Hexadec-1-ene
- Cas Number:
- 629-73-2
- Molecular formula:
- C16H32
- IUPAC Name:
- hexadec-1-ene
- Details on test material:
- not applicable
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not applicable
Sampling and analysis
- Details on sampling:
- not applicable
Test solutions
- Vehicle:
- no
- Details on preparation of test solutions, spiked fish food or sediment:
- not applicable
Test organisms
- Test organisms (species):
- Pimephales promelas
- Details on test organisms:
- not applicable
Study design
- Route of exposure:
- aqueous
- Test type:
- not specified
- Water / sediment media type:
- natural water: freshwater
Test conditions
- Hardness:
- not applicable
- Test temperature:
- not applicable
- pH:
- not applicable
- Dissolved oxygen:
- not applicable
- TOC:
- not applicable
- Salinity:
- not applicable
- Details on test conditions:
- not applicable
- Nominal and measured concentrations:
- not applicable
- Details on estimation of bioconcentration:
- not applicable
Results and discussion
Bioaccumulation factor
- Type:
- other: log BCF
- Value:
- 4.37 dimensionless
- Basis:
- not specified
- Remarks on result:
- other: based on a log Kow 8.06
- Details on kinetic parameters:
- not applicable
- Metabolites:
- not applicable
- Results with reference substance (positive control):
- not applicable
- Details on results:
- not applicable
- Reported statistics:
- not applicable
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The calculated log BCF is 4.37.
- Executive summary:
An experimental BCF is not available for 1 -hexadecene. In the absence of measured data the use of a QSAR to predict the BCF is an appropriate technique to use. The use of the parabolic bioconcentration factor for aquatic organisms QSAR recommended in the Technical Guidance Document (2003) is appropriate for 1 -hexadecene as its log Kow falls within the applicability domain of the model.
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.