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EC number: 500-018-3 | CAS number: 9005-64-5 1 - 6.5 moles ethoxylated
- 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
Acute toxicity:
Oral: based on a weight of evidence approach, all available acute oral toxicity studies on the test substance resulted in acute oral LD50 in rats greater than 2000 mg/kg bw.
Inhalation (OECD 403), rat, 4 hour exposure: LD50 > 5.1 mg/L
Dermal: no study available
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Quality of whole database:
- The available information on the test substance comprises studies which each alone are regarded insufficient for assessment (Klimisch score 4). However, the information from these independent sources is consistent and provides sufficient weight of evidence for hazard assessment leading to an endpoint conclusion in accordance with Annex XI, 1.2, of Regulation (EC) No 1907/2006. Therefore, the available information as a whole is sufficient to fulfil the standard information requirements set out in Annex VII, 8.5, of Regulation (EC) No 1907/2006.
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Quality of whole database:
- The available information comprises an adequate and reliable study (Klimisch score 1), and is thus sufficient to fulfil the standard information requirements set out in Annex VII, 8.5, of Regulation (EC) No 1907/2006.
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Oral
For sorbitan monolaurate, ethoxylated (<2.5 EO, Polysorbate 21, CAS 9005-64-5) data is available for polysorbates with different numbers of oxyethylene-groups in the molecule and is considered in a weight of evidence for the hazard assessment together with sorbitan monolaurate, ethoxylated (20 EO, Polysorbate 20, CAS 9005-64-5). For polysorbate 21 a secondary source with very limited documentation is available which defines a LD50 >33800 mg/kg bw without further information (Elder 1985). For polysorbate 20 oral acute toxicity data is available for rats and mice (Bartsch 1976). 5 male and 5 female Sprague-Dawley rats as well as 5 male and 5 female SPF-NMRI mice were treated with 30 mL/kg bw test substance, corresponding to 32850 mg/kg bw (calculation based on a density of 1.095 g/cm³, see chapter 4.4). Death occurred within 24h, but no further details were given neither on clinical signs, body weight changes or gross pathology. The LD50 was set at 32850 mg/kg bw. Furthermore, polysorbate 20 was tested in a standard acute method with 57 male rats and 47 hamsters, respectively, dosed with concentrations of 36700 and 18000 mg/kg bw, respectively (Eagle 1956). The animals were observed for 7 days. No further details were given on mortality, clinical signs, body weights and gross pathology and the LD50 was determined to be 36700 for rats and 18000 mg/kg bw for hamsters.
Inhalation
An acute inhalation toxicity study was performed with sorbitan monolaurate, ethoxylated (<2.5 EO, Polysorbate 21, CAS 9005-64-5) according to OECD 403 under GLP conditions. Five male and female Wistar rats each were once exposed via nose to 5 mg/L to an aerosol of the test substance for 4 hours (Evonik 2012). No mortality occurred and no clinical signs were observed during the exposure and in the following observation period of 14 days. Body weight gain in males and females was within the expected range and no abnormalities were found at macroscopic post mortem examination of the animals. The LC50 was therefore set to be higher than 5 mg/L.
Dermal
No reliable data on dermal toxicity of sorbitan monolaurate, ethoxylated (<2.5 EO, Polysorbate 21, CAS 9005-64-5) is available. However, one poorly documented dermal acute toxicity study was published by the CTFA performed similar to OECD 402 which revealed a LD50 >3000 mg/kg bw for polysorbat 20 in albino guinea pigs as no clinical signs or adverse findings were determined in gross and histopathology after topical exposure to 3000 mg/kg bw for 24 hours.
Justification for selection of acute toxicity – oral endpoint
Hazard assessment is based on the weight of evidence from all available studies on the test substance.
Justification for selection of acute toxicity – inhalation endpoint
There is only one study available.
Justification for selection of acute toxicity – dermal endpoint
No study required since exposure of humans via dermal uptake is unlikely taking into account the physico-chemical properties of the substance and QSAR prediction.
Justification for classification or non-classification
The available data on acute toxicity (oral and inhalation) of the test substance do not meet the criteria for classification according to Regulation (EC) 1272/2008 and Directive 67/548/EEC, and are therefore conclusive but not sufficient for classification.
No data on acute dermal toxicity is available.
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