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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 931-330-1 | CAS number: 69227-24-3
- 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
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Endpoint summary
Administrative data
Description of key information
Adsorption / desorption
The average Koc value of 1469 was retained for risk assessment purposes.Additional information
Adsorption / desorption
The soil adsorption and desorption potential (Koc) of the test substance, C8-18 and C18-unsatd. MEA, was estimated using the Molecular Connectivity Index (MCI) and Log Kow methods of the KOCWIN v 2.01 program (EPISuite v 4.11). Since the test substance is an UVCB, the Koc values were estimated for individual constituents using SMILES codes as the input parameter. Using the MCI and log Kow methods, the predicted Koc values for all the constituents were estimated to range from 21.37 to 8636 L/kg and 15.71 to 8165 L/kg respectively. The corresponding log Koc values ranged from 1.32 to 3.93 and 1.19 to 3.91 (US EPA, 2019). This indicates a negligible to moderate adsorption potential (US EPA, 2012). Since not all constituents meet the MW and structural fragment molecular descriptor domain criteria as defined in KOCWIN v 2.01 user guide of EPI Suite TM, the Koc predictions were considered to be less accurate. Given that the constituents are structurally very similar and vary only in the carbon chain length, a weighted average value, which considers the percentage of each constituent in the substance, was calculated to dampen the errors in predictions. The weighted average Koc (log Koc) values were calculated as1625.52 L/kg (log Koc=3.21) and 1312.66 L/kg (log koc= 3.11), using the MCI and log Kow methods respectively. Based on the above information, the test substance is expected to have a moderate adsorption potential (US EPA, 2012) to soil and sediment, leading to slow migration to ground water. Overall, the KOC predictions for the test substance using KOCWIN model of EPI Suite TM can be considered to be reliable with moderate confidence.
The average Koc value of 1469 was retained for risk assessment purposes.
Furthermore, after discussion with ECHA in the frame of a Dossier Improvement Action Plan (DIAP), Koc testing according to OECD Guideline 106 is planned with the read across substance C16 MEA in order to support the modelling results obtained with EPISuite across all MEA-FAA substances.
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.
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