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EC number: 268-500-3 | CAS number: 68109-88-6
- 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

Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.003 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 150
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 0.46 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- 0.3 × 1/0.38 × 6.7/10 × 0.5 [50% oral abs rat / 100% inhalation abs hum] × 1.75 [ratio of MW to the read across substance]
- AF for dose response relationship:
- 1
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from subacute study to chronic exposure value in line with Table R.8-5 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- Justification:
- Differences in species addressed in calculation of dose descriptor starting point
- Justification:
- Differences in species addressed in calculation of dose descriptor starting point
- AF for intraspecies differences:
- 5
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for the quality of the whole database:
- 2
- Justification:
- Limited information on chronic, reproductive and developmental toxicity. (OECD 422 study on highly similar read across substance only)
- AF for remaining uncertainties:
- 2.5
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.044 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 600
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 26.25 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- 0.3 × 50 [oral absorption rat 50%/dermal absorption human 1%] × 1.75 [ratio of MW to the read across substance]
- AF for dose response relationship:
- 1
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from subacute study to chronic exposure value in line with Table R.8-5 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value in line with Table R.8-3 and Appendix R. 8-2, part 2, example B5 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- Justification:
- Differences in species addressed in calculation of dose descriptor starting point
- AF for intraspecies differences:
- 5
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for the quality of the whole database:
- 2
- Justification:
- Limited information on chronic, reproductive and developmental toxicity. (OECD 422 study on highly similar read across substance only)
- AF for remaining uncertainties:
- 2.5
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - workers
Dioctyltin bis-(ethylmaleate) is not acutely toxic after oral administration, as the LD50 values are higher than 2000 mg/kg bw, and as high as 6000 mg/kg. Dioctyltin bis-(ethylmaleate) did show irritating properties to both skin and eye when tested in vivo, but there is no dose response data. The read across substance dioctyloxostannane did not produce any sensitisation when tested in a Local Lymph Node Assay in mice. Therefore acute DNELs for systemic effects or acute and long-term DNELs for local effects are not possible to define.
In a 14-d oral (dietary) range finding study females treated at 500 mg/kg in the diet showed body weight loss during the first 3 days of treatment. Compared to the 4 control animals which gained a mean of 8 g, the treated 4 females had a mean loss of 3.57 g/ Examination of food consumption data revealed that these animals ate approximately 43 % less food than controls (in terms of g/animal/day). On this basis, it cannot be excluded that the effect on body weight was due to palatability of the treated diet instead of acute toxicity. This is supported by the fact that effects on body weight and/or food consumption at the highest tested dosage of 250 ppm were observed only later in the main study. Therefore, no acute DNELs for acute systemic effects are considered necessary.
Based on results of in vitro and in vivo studies, on Dioctyltin bis-(ethylmaleate) and the read across substance dioctyloxostannane is considered not to possess any genotoxic potential.
A single repeat-dose combined reproductive/developmental toxicity study on the read across substance dioctyloxostannane was available, performed in rats. As the only suitable study available Waalkens-Berendsen DH (2004) was used as the starting point for DNELs setting.
An additional safety factor of 2 has been applied, because even though the majority of the data are new high quality studies performed in line with good laboratory practices and current standardised guidelines the data was on the read across substance dioctyloxostannane.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.001 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 300
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 0.23 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- 0.3 × 1/1.15 × 0.5 [rat oral abs 50%/human inhalation abs 100%] × 1.75 [ratio of MW to the read across substance]
- AF for dose response relationship:
- 1
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from subacute study to chronic exposure value in line with Table R.8-5 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- Justification:
- Differences in species addressed in calculation of dose descriptor starting point
- Justification:
- Differences in species addressed in calculation of dose descriptor starting point
- AF for intraspecies differences:
- 10
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for the quality of the whole database:
- 2
- Justification:
- Limited information on chronic, reproductive and developmental toxicity. (OECD 422 study on highly similar read across substance only)
- AF for remaining uncertainties:
- 2.5
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.022 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 1 200
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 26.25 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- 0.3 × 50 [oral absorption rat 50%/dermal absorption human 1%] × 1.75 [ratio of MW to the read across substance]
- AF for dose response relationship:
- 1
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from subacute study to chronic exposure value in line with Table R.8-5 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value in line with Table R.8-3 and Appendix R. 8-2, part 2, example B5 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- Justification:
- Differences in species addressed in calculation of dose descriptor starting point
- AF for intraspecies differences:
- 10
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for the quality of the whole database:
- 2
- Justification:
- Limited information on chronic, reproductive and developmental toxicity. (OECD 422 study on highly similar read across substance only)
- AF for remaining uncertainties:
- 2.5
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 1 200
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 0.5 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- 0.3 × 1.75 [ratio of MW to the read across substance]
- AF for dose response relationship:
- 1
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from subacute study to chronic exposure value in line with Table R.8-5 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value in line with Table R.8-3 and Appendix R. 8-2, part 2, example B5 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- Justification:
- Differences in species addressed in calculation of dose descriptor starting point
- AF for intraspecies differences:
- 10
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
- AF for the quality of the whole database:
- 2
- Justification:
- Limited information on chronic, reproductive and developmental toxicity. (OECD 422 study on highly similar read across substance only)
- AF for remaining uncertainties:
- 2.5
- Justification:
- Default value in line with Section R.8.4.3.1 of Chapter R.8 of Guidance on information requirements and chemical safety assessment
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - General Population
The same endpoint used for workers was selected for setting the long-term DNELs for the general population. The larger assessment factor for intraspecies sensitivity was considered adequately protective for the more sensitive population.
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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