Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 233-797-0 | CAS number: 10361-82-7
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
No studies about Samarium chloride were available, but studies about analogue compounds:
With regard to the total hardness and Ca2+ content, a EC50 (48 h) value of 2.083 mg/L (derived in ASTM medium according to OECD 202 with Daphnia carinata) should be used for the classification of Samarium chloride, based on the studies with the analogue Lanthanum chloride.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 2.083 mg/L
Additional information
The acute toxicity of Lanthanum chloride on Daphnia carinata was investigated in three different media according to OECD 202 (Barry and Meehan 2000). Depending on the used media the EC50 values were strongly different.
The investigation using tap water (TW) as test medium with a low total hardness (22 mg/L CaCO3) showed a 48 h EC50 of Lanthanum chloride of 0.076 mg/L. Following this value the 48 h EC50 of 0.086 mg/L was measured in Daphnia water (DW), based on diluted sea water having a total hardness of 98 mg/L CaCO3. In contrast, the 48 h EC50 of Lanthanum chloride in the ASTM standard medium with the highest total hardness (160 mg/L CaCO3) was 2.083 mg/L (see table below). The results showed that the hardness of the test medium reveals a significant influence on the toxicity of Lanthanum chloride on Daphnia carinata.
The three media varied clearly in source and chemical composition, so without extensive testing of the various components, it is not possible to figure out the factors affecting toxicity. Nevertheless, it is well established that carbonate hardness can modify the toxicity of metals to aquatic organisms (for example Cooney, 1995, Yim et al. 2006) and this may be one important factor in determining the toxicity of Lanthanum chloride to Daphnia. The total calcium concentration of the test water may be another factor affecting the toxicity because La3+ behaves much like Ca2+ in biological systems (Evans, 1983). Hardness above 140 mg/l (as CaCO3) for testing on cladocerans is recommended by Cowgill (1990). Tests at this level and above have demonstrated reproductive performance in compliance with the validity criteria.
Compared to the tap water, the Daphnia medium and the Elendt M4 and M7 medium the hardness of ASTM medium is moderate and compatible to standard test conditions.
Since the test result which is the most related to standard conditions should be taken for classification consideration, the 48 h effect concentration of 2.083 mg/L tested in the ASTM medium is applied for the classification of Lanthanum chloride.
The following table shows the total hardness of the three tested media in comparison with Elendt M4 and M7 medium proposed by the OECD 202 Guideline:
Medium |
Total hardness (as mg/L of CaCO3) |
48-h EC50 mg/L |
Tap water (Barry and Meehan, 2000)) |
22* |
0.076 |
Daphnia water (Barry and Meehan, 2000) |
98* |
0.086 |
ASTM medium (ASTM, 1992) |
160* |
2.083 |
Elendt M4 and M7 medium (OECD, 202) |
approx. 250** |
- |
* measured
** theoretical value
Toxicity data for marine species are not available.
Cooney, J.D. (1995). Freshwater tests. In: Rand, G.M. (Ed.), Fundamentals of Aquatic Toxicology. Effects, Environmental Fate, and Risk Assessment, second ed..& Francis,, pp. 71-98.
Long KE et al. (2004). The effects of low hardness and pH on copper toxicity to Daphnia magna.Environ Toxicol Chem.2004 Jan;23(1):72-5.
Evans, C.H. (1983). Interesting and useful biochemical properties of lanthanides. TIBS December, 445 -449.
Cowgill, U.M. and Milazzo, D.P. (1990) The sensitivity of two cladocerans to water quality variables: salinity and hardness. Arch. Hydrobiol., 120(2): 185-196.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.