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EC number: 239-622-4 | CAS number: 15571-58-1
- 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
Description of key information
Additional information
The aquatic toxicity profile of DOTE has been well characterized through several short-term tests and one long-term Daphnia reproduction test. The analysis of the existing data tends to demonstrate that test implementation is complex based on DOTE’s intrinsic properties such as low water solubility and in water. The protocols were designed to address those technical issues.
In the key study conducted in fish, a Water Accommodated Fraction (WAF) was prepared at a loading rate of 100 mg/L and subsequent dilutions containing 0.1, 1.0 and 10 % of the WAF were also prepared. DOTE induced no visible effects in zebra-fish (Brachydanio rerio) at or below a WAF prepared at the loading rate of 100 mg/L over 96 hours. Based on average measured concentrations the NOEC corresponded to 24.8 mg DOTE per litre (3.91 mg tin per litre).
The analytical methodology followed was the analysis of total tin, from which the DOTE concentration was calculated. In this context, the 96 h LC50 > 24.8 mg/L, therefore no effects were observed up to the water solubility limit of DOTE.
In the key study conducted in daphnia, it can be concluded that the 48 hour acute median effective concentration (EC50) of DOTE on Daphnia is 24.12 mg/L
In the key long-term Daphnia reproduction test (21 days) daphnids were exposed to the test material at concentrations of 33, 134, 286, 1448 and 3213 µg/L. Effects were noted at the two highest test concentrations; however it was determined that the effects cannot necessarily be attributed to the parent compound. It was therefore concluded that up to the water solubility of DOTE there is no toxicity. The NOEC was determined to be 0.286 mg/L.
The study was conducted with a test item containing ca. 3 -4 % of Ethylhexylthioglycolate (EHTG, CAS: 7659 -86 -1, EC: 231 -626 -4) as impurity EHTG is better soluable in water as DOTE and shows the following ecotoxicity: EC50 (48 h) Daphnia = 0.38 mg/L EC50 Algae = 0.41 mg/L and is thus classified as Aquatic Acute 1 H400 and Aquatic Chroinic H410 Is likely that the observed effects in the study are caused or exacerbated by the impurity EHTG
In the Key study withPseudokirchneriella subcapita and under the experimental conditions employed, it can be concluded that the growth rate ErC50and inhibition in the yield EyC50for the test item DOTE was greater than 100.0 mg/L.The No Observed Adverse Effect Concentration (NOAEC) over the 72 hours exposure period was also greater than 100.0 mg/L of DOTE.
The 3 hour EC50 for DOTE for inhibiting the respiration of aerobic wastewater bacteria has been determined to be > 100 mg/L.
Discussion
In several of the studies, exposure concentrations were not stable over the test period. Loss of the test material may be due to adsorption onto test vessels or incorporation of the test material in the algae biomass. The test material is poorly soluble in water but contains reactive ligands that can be readily hydrolysed in water, resulting in more-soluble compounds (e.g., hydroxides and oxides). Organotin impurities, including these hydrolysis reaction products, will be present in solution along with the named substance. At least some of these impurities are more soluble in water than the named substance. Poor solubility and the occurrence of hydrolysis reactions present significant challenges to testing organotin compounds in aqueous solutions. It is highly probable that any toxicity seen is not entirely due to the named substance only.
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