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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 212-791-1 | CAS number: 870-08-6
- 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
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
Information describing the potential behaviour of the test substance within the body during the early phase of biotransformation was presented in Schilt & Zondervan-van den Beuken (2004) in an in vitro, non pre-validated, simulated gastric hydrolysis test. The study was performed and reported to a high standard and as such was assigned a reliability score of 2 in accordance with the criteria as outlined in Klimisch (1997) for assessing the quality of data. Under the conditions of the test, it was not possible to measure the hydrolysis of the test substance due to the difficulties presented with the analytical procedures and the physico-chemical properties of the test substance. It was concluded that DOTO would not fully hydrolyse in the test system.
In accordance with point 8.8.1 of column 1 (Standard Information Required), Annex VIII of REACH (Regulation EC No. 1907/2006), assessment of the toxicokinetic behaviour of the substance is performed to the extent that can be derived from the relevant available information. A toxicokinetic assessment was performed based on the available physical-chemical data and toxicological information available. Further testing for the assessment of toxicokinetic behaviour is omitted on this basis.
Toxicokinetic Assessment of the Substance dioctyltin oxide (DOTO)
1.0 Introduction
Physico-chemical properties and the results of in vitro studies and in vivo acute and repeat dose toxicity studies for dioctyltin oxide (DOTO – CAS No. 870-08-6) have been used to determine a toxicokinetic profile.
2.0 Physico-chemical properties
DOTO is a colourless to off-white/white odourless solid and has the molecular formula C16H34OSn with a molecular weight of 361.1506 g/mol. It is very sparingly water soluble (0.0000152 g/L at 20 °C) with an estimated log Pow value of 9.26. Due to technical difficulties with the analytical methods appropriate for this substance, including sensitivity and the poor solubility of the registered substance, not only in water, but also in organic solvents, it was not possible to determine its hydrolytic stability.
3.0 Absorption
3.1 Oral absorption
In an in vitro study simulating gastric conditions to determine the extent of hydrolysis to dioctyltin chloride, no meaningful results were obtained, because DOTO was extremely insoluble in the test system and only partially hydrolysed. It was noted that the particle size of the test substance influenced the level ofdioctyltin chlorideformed and was considered to be the cause of the high variability between replicates. Increased temperatures higher than 37 °C (up to 60 °C) increased the speed of hydrolysis. The percentage of hydrolysis never exceeded 55 % and in most cases was considerably lower (2-5 %); it was concluded that DOTO would not hydrolyse to an appreciable extent under gastric conditions. DOTO appeared to be relatively resistant to the simulated gastric hydrolysis.
The available information on acute oral toxicity supports a limited oral absorption, as the reported LD50values are generally higher than a limit dose of 2000 mg/kg bw (up to greater than 6000 mg/kg bw). Some oral absorption is also demonstrated by results of a fully compliant OECD 422 study, using the dietary route of exposure, because treatment at a dietary level equivalent to 1.5-2.4 mg/kg/day resulted in adverse effects on thymus; at a higher dietary concentration (equivalent to 11-17 mg/kg/day) treatment also affected reproductive parameters and some signs of liver involvement were also noted.
As a worst-case estimate, for risk assessment purposes DOTO is considered to be absorbed at 50 % or less following oral administration. For risk assessment purposes 50 % is assumed.
3.2 Dermal absorption
No information is available on dermal absorption. DOTO is a
solid particulate (i.e. with an effective MW of many times the molar
mass of 361.1506 g), is poorly soluble in water (0.0000152 g/L at 20
°C), and has an estimated log Pow value of 9.26. All these factors
indicate the rate of transfer between the stratum corneum and
the epidermis will be slow, and will limit absorption across the
skin. In accordance with criteria in Chapter R.7c: Endpoint specific
guidance (Guidance on information requirements and chemical safety
assessment) a default dermal absorption value of 10 % may be assigned
for soluble substances with a MW >500 and log Pow >>4. In this
case the material is an insoluble particulate solid (insoluble
material is considered in the guidance to have practically no
absorption) so absorption would be considerably lower than 10 %, and a
value of 1 % is considered appropriate for risk assessment purposes.
In the dermal toxicity study on Dioctyltin dilaurate from Blackburn et al., there was no absorption of tin into the blood of the study animals found. The stubstance Dioctyltin dilaurate hydrolyses at once in contact with water into Dioctyltin oxide and Lauric acid.
Thus can be concluded, that there is no dermal absorption of DOTO.
3.3 Inhalation absorption
No information is available on inhalation toxicity of the substance, or on inhalation absorption.The particle size distribution of the substance was investigated using a method based on a procedure designed to be compatible with that given in `Particle Size Distribution, Fibre Length and Diameter Distribution', June 1996 European Commission technical guidance document. Sieving apparatus was used in a screening test to investigate particle size of 100 µm. A cascade impactor was then employed to investigate particles in the size range of 0.3 to 10 µm. The study showed that most part of DOTO would not reach the lower tract of the respiratory system, as the proportion of the test material having an inhalable particle size of <100 µm was 15.2 %; that having a thoracic particle size of <10.0 µm was 1.21 % and that having a respirable particle size of <5.5 µm was 0.40 %.
As a worst case and really conservative approach, the inhalation absorption in humans is considered to be complete (100 %) for risk assessment purposes.
4.0 Distribution
Results of the OECD 422 study suggest that once absorbed DOTO is widely distributed within the body, as the target organ was the thymus and, at higher doses, the reproductive system and the liver. Given the high estimated log Pow and the extremely low water solubility, micellular solubilisation may play a major role for absorption, and preferential partition to tissues with high lipid content.
5.0 Metabolism
No information is available. Given the length of the chain (octyl), DOTO is not anticipated to undergo significant biotransformation.
6.0 Elimination
Unchanged DOTO is expected to be excreted mainly via the faeces.
A bioaccumulation study in fish with a structurally related substance determined a BCF of >100. No upper limit appears to have been verified hence it is not possible to estimate the extent of elimination of the material from fatty tissues.
7.0 Conclusion
For risk assessment purposes, moderate absorption following oral administration is assumed (50 %) for DOTO, but it is estimated to be less absorbed following dermal exposure (1 %), and completely absorbed following inhalation (100 %).
The substance is considered to be widely distributed within the body, hardly metabolised, and excreted mainly unchanged in the faeces.
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.