Registration Dossier
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EC number: 214-946-9 | CAS number: 1222-05-5
- 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
Additional information
HHCB does not mineralise under the conditions in screening tests for readily biodegradation (KEY study Jenkins 1991).
From other biodegradation studies in water and/or sediment it is concluded that primary biodegradation to a series of more polar metabolites takes place, with HHCB-lactone and hydroxycarboxylic acid as likely intermediates. These substances still contain the same amount of organic carbon and only a small fraction of the theoretical oxygen demand has been incorporated. Thus this metabolism is in agreement with the observed low degree of mineralisation.
From the studies with activated sludge spiked with 14C-radio-labelled HHCB in batch experiments (a.o. Schaefer 2005) it is concluded that the parent substance was transformed to a series of polar metabolites. In general the radio-labelled parent HHCB disappeared with half-life values in activated sludge of 10 – 15 hours (Schaefer 2005). In the river die-away test with 5 µg/l the parent HHCB disappeared with a half-life of 100 hours (4 days, KEY study Schaefer 2005).
Field measurements on sludge amended soil indicate that HHCB disappeared almost completely from soil within one year. The residues in soil after one year ranged from below 10% to 14% of the initial concentrations (Envirogen 1998). The half-life of 105 days in the sludge amended soil test is most relevant for the fate of HHCB in soil in the EUSES model, whereas 79 days was noted for the sediment (KEY study Envirogen 1998).
Subsequently, for the environmental risk assessment, HHCB may be considered as 'inherently biodegradable, not fulfilling criteria' (terminology of the EU-TGD, EC 2003). For surface water, sediment and soil, the PECs used on the risk assessment will be calculated using conservative biodegradation rate constants expressed as half-life times: 60 d in surface water (20 ºC) and 150 d in the soil and sediment compartments (12 ºC). For the PBT assessment, the studies of Schaefer (2005) shows that HHCB is 'not P' in water, whereas the studies of Envirogen (1998) show that HHCB is 'not P' in sediment and in soil.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.
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