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EC number: 285-349-9 | CAS number: 85085-18-3
- 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
Repeat dose studies for this substance have not been carried out on test animals for oral, dermal or inhalation routes of exposure and waivers have been justified for non-testing.
For oral exposure an estimate of the NOAEL has been made based on results from a 90 day study for Laponite type 2, a read-across material of similar structure.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 50 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
Additional information
Of relevance is a 90 day study carried out in 1973 on Laponite type 2, which is a similar structure to Laponite type 1 and consequently a “read-across” material. The main difference between the two materials being that type 1 contains fluoride in the clay lattice. Fluoride is known to be orally toxic above specified levels and so some assumptions must be made.
The 90 day chronic test was designed to evaluate the repeat dose oral toxicity of Laponite on rats over a period of 3 months. The material was dispersed in deionised water and the rats were fed by intubation. The rats were split into four groups, even numbers of male/female. Group 1 was the control group, (just water), group 2 was low dose (5mg/kg bw), group 3 was medium dose (50mg/kg bw) and group 4 was high dose (500mg/kg bw). The high dose group saw some premature deaths and these were found to be due to the fact that the Laponite forms a gel at high dose and this had accumulated in the animal’s digestive system and had not been digested. This level of dosing would not be permitted under today's controls. For surviving rats at necropsy, there were no signs of abnormalities relating to the oral dosing of the Laponite. The high dosage group resulted in half of the rats failing to survive to completion of the test but all rats in the other two groups (with the exception of 1 in the low dose group whose death was not attributed to the treatment) all survived. No systemic toxic effect as ascertained by blood analysis and histopathological examination were observed, even in the high dose rats.
If the test were to be repeated with Laponite type 1, it is known that under the low pH conditions of a rat’s stomach that the material reverts back to the individual lattice components, including fluoride as F-.
For NaF, the LOAEL (lowest-observed-adverse-effect-level) on rats in a repeat dose 28 day study done to OECD Guideline 407 (as reported in the REACH dossier for sodium fluoride) is 10 mg/kg bw/day as NaF, which equates to 4.5 mg/kg bw/day as F. This would be the equivalent of ~50 mg/kg bw/day for Laponite type 1 if all the fluoride in the material were to be absorbed through the stomach.
Therefore an estimate can be made that the NOAEL for Laponite type 1 in the worst case scenario that all fluoride became accessible for absorption under repeat dose testing could be ~ 50 mg/kg bw/day
Justification for classification or non-classification
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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