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EC number: 701-197-2 | 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

Endpoint summary
Administrative data
Description of key information
Additional information
General consideration
The scientifically accepted calculation tool EPIWIN (by US-EPA) was used to determine the phototransformation behaviour in air, hydrolysis, the biodegradation potential in water, aquatic bioaccumulation, soil adsorption and the substance specific Henry´s Law Constant (HLC). No GLP criteria are applicable for the usage of these tools, but due to the fact that they are scientifically accepted calculation methods the estimations performed are reliable with restrictions (Klimisch 2) and can be used for the chemical safety assessment. The corresponding software programs of EPIWIN were often used in two variations of the test substance: with and without chlorine in the main component.
Stability
The gas-phase reaction constants and half-lives in the atmosphere predicted by AOPWIN v1.92 differ only a little depending on chlorine and its appearance (Chemservice S.A., 2012). With chlorine the overall OH rate constant is 57.52E-12 cm³/molecules-sec with a half-life of 2.23 hours, whereas without chlorine the rate constant is predicted as 54.44E-12 cm³/molecules-sec with a half-life of 2.36 hours, assuming a 12 h day with an OH rate of 1.5E6 OH/cm³ and 25 °C.
Epoxides were detected as hydrolysable substance class by HYDROWIN v2.00 with half-lives of ~ 44 years and ~ 29 years for the main component with and without chlorine, respectively, at 25 °C and pH 7 (Chemservice S.A., 2012).
Biodegradation
An experiment in order to investigate the ready biodegradability of the test substance was performed according to OECD Guideline 301F, EU Method C.4 -D and US EPA Draft OPPTS 835.3110 over a prolonged time duration of 55 days (Eisner, 2013). At Exposure Day 28 and at test end after 55 days, the mean biodegradation of 1,2,3-Propanetriol, glycidyl ethers amounted to 13 % and 24 % of the COD, respectively. The pass level for ready biodegradability was not reached. In conclusion the test substance is not readily biodegradable.
The aquatic bioconcentration factor (BCF) was predicted as 3.16 L/kg wet-wt by the regression-based estimate of BCFBAF v3.01 (Chemservice GmbH, 2011), indicating that bioaccumulation in aquatic biota can be ruled out.
Transport and distribution
A low potential for soil adsorption is predicted by KOCWIN v2.00, since the organic-normalized sorption coefficient (Koc) was predicted as 10 L/kg (Chemservice GmbH, 2011).
Based on the Bond Method of HENRYWIN v3.20 the Henry´s Law Constant is predicted as 7.11E-12 Pa*m³/mol, whereas the Group Method estimation resulted in a Henry´s Law Constant of 4.72E-17 Pa*m³/mol for the main component with chlorine (Chemservice S.A., 2012). The Henry´s Law Constants for the component without chlorine are predicted as 2.15E-9 Pa*m³/mol and 2.37E-14 Pa*m³/mol concerning both methods, respectively.
Neither monitoring data nor field studies are available for the test substance.
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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