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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 204-617-8 | CAS number: 123-31-9
- 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
Additional information
Phototransformation in air
According to a generally accepted calculation method (AopWin v1.92), the half-life of hydroquinone in the atmosphere due to OH radical degradation is 16.58 hour (24-hr day; 0.5E6 OH/cm3).
Hydrolysis
According to REACH regulation (Annex VIII), the study on hydrolysis does not need to be done if the test substance is readily biodegradable or is poorly soluble in water. Hydroquinone is classified as readily biodegradable, in addition no hydrolyzable groups are present in the molecule.
Phototransformation in water
Hydroquinone is photo-oxidized in aqueous solution forming p-benzoquinone, hydroxy-p-benzoquinone and trihydroxybenzene as products. In natural waters radicals like OH and RO2 are present and can react with organic compounds. Based on an oxidation rate constant for the reaction of hydroquinones with alkylperoxy radicals (RO2•) of 1*10^6 (M*sec)^(-1) and an average environmental concentration of RO2• near surface of 1*10^(-9) M, the half-life of hydroquinone in sunlight exposed natural waters is calculated to be 12 minutes. Considering turbidity and decreasing light intensities in deeper water layers, a 100-times lower concentration of [RO2•] is assumed, leading to a worst-case estimate for the half-life of hydroquinone in surface waters of 20 hours based on photooxidation with RO2• alone (leaving behind other oxidative degradation events as well as biodegradation).
This value is confirmed by the OECD SIDS document (2002) on hydroquinone, which states a half-life in surface water of 20 hours.
Phototransformation in soil
Phototransformation in soil is expected to be of no or minor relevance for the fate of hydroquinone in the terrestrial environment. The test substance is regarded as readily biodegradable and hydroquinone is expected to biodegrade in soil. Therefore, a study on phototransformation in soil is scientifically unjustified.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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