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Diss Factsheets
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EC number: 274-402-1 | CAS number: 70210-05-8
- 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
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Toxicity to aquatic plants other than algae
Administrative data
Link to relevant study record(s)
Description of key information
100 mg/l < ErC50 < 1000 mg/l
EyC50: ca. 100 mg/l
Key value for chemical safety assessment
Additional information
The Read across approach here discussed is based on the structural similarity of the two main components of target and source substances, on their similar composition and biodegradation potential, in order to fulfil eco-toxicological information requirements (toxicity to aquatic plants other than algae).
The inhibitory effects based on the average specific growth rate and the yield (absolute increase in plant size) to the duckweed Lemna minor was
investigated over a period of 7 days.
The test was performed at nominal concentrations of 11.4, 114 and 1140 mg/l of test substance, corresponding to 10, 100 and 1000 mg/l of the active ingredient (AI).
No chemical analysis of the test concentrations was conducted. The determination of the effect concentrations was based on the nominal concentrations of the active ingredient assuming the test item to be stable in medium for the whole test period.
For the endpoint frond number and with respect to growth rate inhibition, the following effects as compared to the untreated controls were observed: 19 % at 100 mg/l and 75 % at 1000 mg/l. No significant effects were observed at 10 mg/l, as determined by Dunnet’s test.
For the endpoint frond number and with respect to yield inhibition, the following effects as compared to the untreated controls were observed: 18 % at 10 mg/l, 41 % at 100 mg/l and 92 % at 1000 mg/l.
Based on these data the median effect concentrations to Lemna minor with respect to growth rate (ErC50) and to yield (EyC50) for the endpoint frond
number was estimated to be 100–1000 and about 100 mg/l nominal concentration, respectively.
The no-observed-effect concentrations to Lemna minor with respect to growth rate (NOErC) and yield (NOEyC) for the endpoint frond number were 10
and <10 mg/l nominal concentration, respectively, as determined by Dunnett's test.
For the endpoint dry weight and with respect to growth rate inhibition, the following effects as compared to the untreated controls were observed: 20 % at 100 mg/l and 67 % at 1000 mg/l. No significant effects were observed at 10 mg/l, as determined by Dunnet’s test.
For the endpoint dry weight and with respect to yield inhibition, the following effects as compared to the untreated controls were observed: 22 % at 10 mg/l, 44 % at 100 mg/l and 90 % at 1000 mg/l.
Based on these data the median effect concentrations to Lemna minor with respect to growth rate (ErC50) and to yield (EyC50) for the endpoint dry
weight was estimated to be about 100 – 1000 and about 100 mg/l nominal concentration, respectively.
The no-observed-effect concentrations to Lemna minor with respect to growth rate (NOErC) and yield (NOEyC) for the endpoint dry weight were 10 and <10 mg/l nominal concentration, respectively, as determined by Dunnett's test.
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