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EC number: 239-581-2 | CAS number: 15535-79-2
- 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

Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
Description of key information
DOTTG is manufactured as a 2.5 -10 % solution in DOTE/DOTI
So the predominat exposure of microorganisms, will be to DOTE or it's degradation products DOTO and EHTG
The corresponding degradation products of DOTTG would be DOTO and Thioglycolic acid.
Studies done on different organotincompounds with thioligand at higher pH demonstrate the stability during manufacturing process, which includes contact to water and to simulate the exposure and behavior in the environment.
Dioctyltins with a thio ligand hydrolyse in acetonitrile/water solutions to form dioctyltin oxide and release the thioligand
The formation of the ligand EHTG could be observed unequivocally, whereas the formation of DOTO was postulated. The DOTO signal intensity remained constant in the experiment, which was attributed to the very low solubility of DOTO. (Yoder 2003)
The study shows, that dioctyltins in solution react rapidly with water to form Dioctyltin oxide and the ligand. The scenario is relevant for any dissolved dialkyltin compounds which are dissolved in water, e.g. during sewage treatment.
So both the study on DOTE as well as on DOTO are considered relevant for the assessment of the toxicity to microorganisms
Roulstone (2012), OECD 209 (read-across from dioctyltin oxide); EC50 > 1000 mg/L, NOEC 1000 mg/L.
Baumann (1992), Directive 87/302/EEC, part C (read across from DOTE) EC50 >= 100 mg/L
The ligand which is released during hydrolysis of dialkyltin thioglycolates (Yoder 2003) is Ethylhexyl thioglycolate (EHTG)
It is is self-classified as Aquatic Acute 1 and Aquatic Chronic 1.
The ligand of DOTTG, Thioglycolic acid is not classified for the environment and thus does not pose any additional risk for the environment when released from DOTTG by hydrolysis
It degrades in water by fast oxidation to dithiodiglycolate.
Based on the physico-chemical properties of thioglycolic acid and salts (high solubility and low Log P), it is considered that they are not expected to adsorb to suspended solids, sediments and soils and are mobile in soil
Thioglycolic acid and its main oxidation product, the diammonium dithiodiglycolate, it can be considered that thioglycolic acid and its salts are ready biodegradable and do not raise concern in terms of persistency.
Thioglycolic acid and its salts are highly soluble in water (> 1000 g/L at 20°C) (Sablowski, 2007b; reliability 2) and have a partition coefficient octanol-water equal to -2.99 at 22°C and pH 7. Therefore thioglycolic acid is not expected to bioaccumulate according to technical guidance documents
RAC (RAC 47, November 2018) came to an opinion that DOTE fulfils the CLP criteria for classification as Aquatic Acute 1 and Aquatic Chronic 1.
Since DOTTG is manufactured only in 2.5-10 % in DOTE this opinion ios relavant for the classifcation of DOTTG.
The RAC opinon on the aquatic classification of DOTE has been adopted for DOTTG.
Any different result of a study on pure DOTTG would not change the adopted classifcation of the manufactured and marketed form of DOTTG
Key value for chemical safety assessment
- EC50 for microorganisms:
- 1 000 ng/L
- EC10 or NOEC for microorganisms:
- 1 000 mg/L
Additional information
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