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Diss Factsheets
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EC number: 204-104-9 | CAS number: 115-77-5
- 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
The substance Pentaerythritol is stable to hydrolysis, i.e. estimated half-life of greater than one year.
A number of resources are available to evaluate the ready biodegradability of pentaerythritol. Several tests employing different test methodologies are presented. The two factors that influenced the rate of degradation were inoculum concentration and pre-adaptation of inoculum.
In the majority of tests pentaerythritol was observed to degrade by at least 60% over 28 days under all conditions. The biodegradation usually occurred after a brief lag time and achieved 60% within 10 days (Malta and Blom, 1990; Birch and Fletcher, 1991). When tested against activated sludge that was pre-adapted to industrial chemicals (Zahn-Wellens), the rate of biodegradation increased and no lag time was observed. After 28 days, nearly 100% biodegradation was observed (ANOX, 1994).
Based on the results of Birch and Fletcher, the test substance is readily biodegradable when the inoculum concentration is at least 0.05% vol/vol of secondary effluent or ~ 3 x 105viable cells/litre. This concentration is well within the recommended concentration provided in the relevant guideline and is far below that usually encountered in a standard STP.
Based on several studies, pentaerythritol is considered to be readily biodegradable. As such removal in the STP is expected to be efficient with the major fraction of any emissions being removed at this point. Any emissions to soil, surface water and sediment would be expected to degrade rapidly by microbial action.
In accordance with REACH Annex IX column 2, the degradation simulation testing in water and/or sediment and in soil does not need to be conducted as the substance is readily biodegradable.
The log Kow pentaerythritol is reported to be -1.7 (see Section 4.7, partition coefficient). The log Kow is below the trigger of 3 and therefore pentaerythritol is not expected to bioaccumulate in living organisms.
The substance pentaerythritol can be expected to have a low potential for adsorption to soil and little propensity to partition to sediment. Pentaerythritol has a low octanol-water partition coefficient, log Kow = -1.7. As such for the purposes of environmental modelling the Koc can be estimated to be less than 10.
Additional information
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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