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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 271-360-6 | CAS number: 68551-08-6
- 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
Description of key information
Hydrolysis:
Aliphatic alcohols are resistant to hydrolysis because they lack a functional group that is hydrolytically reactive.Therefore, this fate process will not contribute to a measurable degradative loss of this substance from the environment.
Phototransformation in air:
The photodegradation half-life of this substance as mediated by OH-attack is estimated as0.62days or 7.4 hours based on a 12-hour sunlight day.
Phototransformation in water and soil:
Aliphatic alcohols will not undergo direct photolysis and this fate process will not contribute to a measurable degradative loss of this substance from the environment.
Biodegradation:
Alcohols, C9 -C11-branched is readily biodegradable and hasbeen shown to biodegrade to a significant extent in a test of ready biodegradability (71% in 28 days) using standard OECD test guidelines. Therefore, biotic degradation will significantly contribute to the loss of this substancefrom the environment.
Bioaccumulation:
Experimental data along with the biochemical evidence suggest that this substance has a very low potential for bioconcentration in aquatic species and is not expected to bioaccumulate.
Adsorption / desorption:
The soil adsorption partition coefficient Koc of 687 (log Koc = 2.84) was estimated for Alcohols, C9-C11-branched using a log Kow method and the measured log Kow.
Distribution modelling:
Alcohols, C9 -C11, branched will partition largely to the soil compartment, followed by the water, air, and minimally to the sediment compartments, based on all available measured data. Volatilization from water and soil is expected to occur at a moderate rate.
Additional information
Hydrolysis:
Hydrolysis
of an organic molecule occurs when a molecule (R-X) reacts with water
(H2O) to form a new carbon-oxygen bond after the carbon-X bond is
cleaved. Mechanistically,
this reaction is referred to as a nucleophilic substitution reaction,
where X is the leaving group being replaced by the incoming nucleophilic
oxygen from the water molecule.
Chemicals that are susceptible to hydrolysis contain functional groups
that can be displaced by a nucleophilic substitution reaction. Substances
that have the potential to hydrolyze include alkyl halides, amides,
carbamates, carboxylic acid esters and lactones, epoxides, phosphate
esters, and sulfonic acid esters. The
lack of a leaving group renders a compound resistant to hydrolysis.
Aliphatic alcohols are resistant to hydrolysis because they lack a
functional group that is hydrolytically reactive.Therefore, this
fate process will not contribute to a measurable degradative loss of
this substance from the environment.
Phototransformation in air:
Alcohols, C9 -C11, branched has the potential to degrade in the atmosphere from hydroxyl radical attack and photodegradation can be a predominant daylight atmospheric degradation process for this substance. The photodegradation half-life of this substance as mediated by OH-attack is estimated as0.62days or 7.4 hours based on a 12-hour sunlight day. The half-life is calculated for a 12 -hr day because it normalizes degradation to standard day-light period during which hydroxyl radicals needed for degradation are generated.
Phototransformation in water and soil:
A conservative approach to estimating a photochemical degradation rate is to assume that degradation will occur in proportion to the amount of light with wavelengths >290 nm absorbed by the molecule. Alkyl alcohols contain molecules that are oxygenated aliphatic compounds, which absorb UV light below 220 nm, a range of UV light that does not reach the earth's surface. Therefore, aliphatic alcohols will not undergo direct photolysis and this fate process will not contribute to a measurable degradative loss of this substance from the environment.
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.