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EC number: 273-066-3 | CAS number: 68937-41-7
- 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
Toxicity to soil macroorganisms except arthropods
The 14-day LC50 estimation for earthworms exposed to the test substance in an artificial soil substrate was determined to be greater than 1000 mg/kg dry soil. The no-observed-effect-concentration (NOEC) was 500 mg/kg, based on reduced body weights in the 1000 mg/kg level.
There was no mortality of adult earthworms exposed to nominal concentrations of Reofos 35 at 62.5, 125, 250, 500, and 1000 mg/kg dry soil for 28 days. Based on body weight and survival data of adult earthworms, the no observed effect concentration (NOEC) was determined to be 1000 mg/kg dry soil, the highest concentration tested. There were no reductions of 50% or greater for the numbers of juveniles produced in the treatment groups in comparison to the pooled control group, therefore the EC50 for reproduction was greater than 1000 mg/kg dry soil, the highest concentration tested. The EC10 for reproduction was determined to be 172 mg/kg dry soil. The NOEC was 250 mg/kg dry soil and the LOEC was 500 mg/kg dry soil, based on the reduced number of juveniles produced.
Toxicity to terrestrial arthropods
In accordance with column 2 of REACH Annex X, Long-term toxicity testing shall be proposed by the registrant if the results of the chemical safety assessment according to Annex I indicates the need to investigate further the effects of the substance and/or degradation products on terrestrial organisms. The choice of the appropriate test(s) depends on the outcome of the chemical safety assessment. The substance does not demonstrate effects in the 3 groups of terrestrial organisms assessed. Hence, it is considered unnecessary to test for this additional endpoint. The substance is not hazardous to terrestrial organisms.
Toxicity to terrestrial plants
Acute
The effects of Durad 310M, incorporated into soil at concentrations of 100, 10, 1 and 0 mg/kg, upon the germination (emergence) and growth of seedlings of wheat (Triticum aestivum), radish (Raphanus sativus)and mung bean (Phaseolus aureus) were determined over periods of 19, 18 and 19 days respectively, representing 14 days after at least 50% emergence of control seedlings.
The LC50 for emergence and EC50 for growth rate were both greater than the highest concentration tested, 100 mg/kg, in all species.
No phytotoxic effects were observed for any of the species tested.
Chronic
In accordance with column 2 of REACH Annex X, Long-term toxicity testing shall be proposed by the registrant if the results of the chemical safety assessment according to Annex I indicates the need to investigate further the effects of the substance and/or degradation products on terrestrial organisms. The choice of the appropriate test(s) depends on the outcome of the chemical safety assessment.
Based on the lack of toxicity within the short term plant study, and the fact that no effects are noted in the other studies, it is proposed that a long term toxicity test in plants is not required.
Toxicity to soil microorganisms
The long-term effects of the test substance on nitrogen transformation activity of soil microorganisms were minimal at concentrations 10, 32, 100, and 318 mg/kg dry soil. There was an observed effect of The test substance on nitrogen transformation activity of soil microorganisms at concentration level 1010 mg/kg dry soil. After 28 days of exposure, the mean nitrate concentration in soil treated at 10, 32, 100, 318, and 1010 mg/kg dry soil exhibited a -1%, 1%, 0%, 2%, and 23% reduction in nitrate formation, respectively, compared to the controls. The EC10 was calculated to be 582.7 mg/L using linear interpolation between concentrations 318 and 1010 mg/L. The EC25 and EC50 were estimated to be >1010 mg/L, the highest concentration tested.
Toxicity to birds
There is sufficient mammalian toxicology available on the substance to preclude the requirements to test for toxicity to birds. As such, this endpoint is waived on the grounds of animal welfare and sufficient information on toxicological properties being available to adequately assess the substance.
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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