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EC number: 201-077-5 | CAS number: 78-04-6
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
The following study was provided as the key study to fulfil the data requirement short-term toxicity to fish:
Hooftman R. N. & De Wolf J. M. (2003). 1,3,2-Dioxastannepin-4,7-dione, 2,2-dibutyl-(dibutyltin maleate, CAS # 78-04-6): Semi-static acute toxicity test with the zebra fish Brachydanio rerio. Testing laboratory: TNO, Project Organisation, Ecotoxicology, Utrechtseweg 48, P. O. Box 360, 3700 AJ Zeist, The Netherlands. Report no.: V4017/03. Owner company: Organotin Environmental Programme (ORTEP) Association, Stabilizer Task Force. Report date: 2003-09-15.
In a semi-static acute toxicity test with the zebra fish Brachydanio rerio study the 96h LC50 for the test material was determined as >5.70 mg/l. The test was performed in two stages, first as a limit test and subsequently as an additional full test.
The study was conducted to the OECD Guideline no. 203 and the EU Guideline no. C.1, and in compliance with the OECD Principles of Good Laboratory Practice.
A further three studies were provided as supporting information.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 5.7 mg/L
Additional information
The following data have been submitted to address the short-term toxicity to fish endpoint:
Hooftman R. N. & De Wolf J. M. (2003). 1,3,2-Dioxastannepin-4,7-dione, 2,2-dibutyl-(dibutyltin maleate, CAS # 78-04-6): Semi-static acute toxicity test with the zebra fish Brachydanio rerio. Testing laboratory: TNO, Project Organisation, Ecotoxicology, Utrechtseweg 48, P. O. Box 360, 3700 AJ Zeist, The Netherlands. Report no.: V4017/03. Owner company: Organotin Environmental Programme (ORTEP) Association, Stabilizer Task Force. Report date: 2003-09-15.
The 96h LC50 for the test material was determined as >5.70 mg/l. The test was performed in two stages, first as a limit test and subsequently as an additional full test.
The following studies were provided as supporting information:
Nagase H, Hamasaki T, Sato T, Kito H, Yoshioka Y & Ose Y (1991). Structure-activity relationships for organotin compounds on the red killifish Oryzias latipes. Applied Organometallic Chemistry 5:91-97.
Results: DBTM - In a semi-static acute toxicity test with the red killifish, Oryzias latipes, conducted according to OECD Guideline 203, dibutyltin maleatewas found to have a 48h LC50 value of 13.12 mg/l.
DBTO - In a semi-static acute toxicity test with the red killifish, Oryzias latipes, conducted according to OECD Guideline 203, di-n-butyltin oxide was found to have a 48h LC50 value of 0.839 mg/l.
Steger-Hartmann T and Wendt B (1998). Acute toxicity of di-n-butyltin oxide (ZK 26385) to the Zebra fish Danio rerio. Testing laboratory: Schering AG, Experimentelle Toxikologie, D-13342, Berlin Germany. Report no.: IC19. Owner company: Schering AG, Experimentelle Toxikologie, Berlin Germany. Study number: TXST19980196. Report date: 1998-12-11.
Result: In a static acute toxicity test according to OECD Guideline 203, 10 Zebra fish (Danio rerio) were exposed to a saturated aqueous solution of di-n-butyltin oxide. No mortality was observed in the control. One fish was found dead after 72 hours of exposure in the saturated solution of di-n-butyltin oxide. During exposure, the fish showed signs of abnormal behaviour nearly at all time points. 10% mortality was observed, therefore di-n-butyltin oxide is of low acute toxicity to fish up to 3.10 mg/l (maximum of solubility, determined on the basis of Total Organic Carbon (TOC) analysis).
Hooftman and De Wolf has been performed using dibutyltin maelate and so is considered the key study for this endpoint.
The study has been performed to the appropriate guideline and to GLP and is allocated a Klimisch score of 1.
Steger-Hartmann and Wendt has been performed using dibutyltin oxide and so is used a supporting information due to the fact that it is known that organotin ligand will hydrolyse to this form over time.The study has been performed to the appropriate guideline and to GLP but is allocated a Klimisch score of 2 as the reliability is reduced for read-across purposes.
The Nagase et al (1991) studies have been allocated a Klimisch score of 4 because of missing information in the study reports and are considered to be supporting studies.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.