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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 902-053-3 | 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
Description of key information
Ethanol:
Fresh water: Readily biodegradable (2 studies), inherently biodegradable (1 study)
Salt water: readily biodegradable (1 study)
Anaerobic conditions: degradable, complete mineralisation (1 study)
Isopropanol:
The substance has a BOD5/ThOD ratio of 0.50, and is therefore considered to be readily degradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
There are no data available for the reaction mass.
Ethanol:
The biodegradation of ethanol was assessed at a number of concentrations using a non-adapted domestic sewage inoculum in a freshwater medium using a 20 day study. Rapid degradation was observed. In a study that used a method based on a proposed improvement to a Sturm guideline study to make it more suitable for volatile substances, ethanol was shown to be readily biodegradable. In both cases, degradation well in excess of 60% was seen with 5 days. Based on the results of these studies, ethanol meets the criteria to be classified as readily biodegradable.
The biodegradation of ethanol was assessed at a number of concentrations using an inoculum prepared from natural salt water and boosted with non-adapted domestic sewage inoculum in an artificial salt water medium. Degradation was observed to a level of 75% over 20 days and 68% in 10 days. This results shows it meets the requirement for designation as readily biodegradable in sea water.
In a study to assess the biodegradability of ethanol under anaerobic conditions, ethanol was exposed to methanogenic bacteria derived from an aquifer slurry. Degradation was followed by measuring the pressure increase through emissions of CH4 and CO2 and, at the end of the study, by GC analysis to quantify the amount of methane produced. After a lag time of 25 -30 days, methane emissions equivalent to 91% mineralisation was eventually seen (after an unquantified time) indicating biodegradability under anaerobic conditions.
The biodegradation data suggests a half life of around 3 days in water, which compares to other an estimated river half life of 6.5 -26 hours and a half life for aerobic degradation of 26 -104 hours.
Isopropanol:
The BOD5 (non-adapted), BOD5 (adapted) and COD of the substance were reported by Bridié et al. (1979) to be 1.19 g O2/g, 1.72 g O2/g and 2.23 g O2/g, respectively. The BOD test was conducted in accordance with the standard dilution method (APHA "Standard Methods" No. 219 (1971)) at 20 ± 1ºC for a period of 5 days. The only deviation from the APHA standard was the addition of 0.5 mg/l allylthiourea in each test to prevent nitrification. 500 ml test solutions were seeded with a filtered 10 ml volume of the effluent from a biological sanitary waste treatment plant. The authors reported that in some cases an adapted seed was prepared and used, although in no case was inducement of adaptation tried exhaustively. Duplicate tests were run on a mixture of glucose and glutamic acid, as recommended in the APHA method, as a means of checking the activity of the inoculum. The COD test was conducted in accordance with the standard potassium dichromate method described in ASTM D 1252 -97 (reapproved 1974). The BOD5/COD ratios from these results are 0.53 (non-adapted) and 0.77 (adapted). As indicated in the REACH Endpoint Specific Guidance section R.7.9.5.1; whereno other measured degradability data are available,BOD5 datacan be used for classification purposes, but where the chemical structure is known, a calculated theoretical oxygen demand (ThOD) value should be used instead of the COD. According to Annex IV of OECD 301, the ThOD of this substance can be calculated to be 2.40 g O2/g, which gives BOD5/ThOD ratios of0.50 (non-adapted) and 0.72 (adapted). The value for non-adapted seed equals 0.5, at which level or above a substance can be considered to be readily degradable.
Therefore it can be concluded that the reaction mass also can be considered readily biodegradable.
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.