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Diss Factsheets
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EC number: 231-887-4 | CAS number: 7775-09-9
- 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 soil macroorganisms except arthropods
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil macroorganisms except arthropods: short-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Not all information necessary is given, no results per concentration given, no analytical monitoring and no GLP. Despite these shortcomings, the results can be used.
- Principles of method if other than guideline:
- Method: other: artificial soil test, laboratory test of the BBA. Resembles OECD Guideline 207
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Eisenia fetida
- Study type:
- laboratory study
- Substrate type:
- other: artificial soil test
- Limit test:
- no
- Total exposure duration:
- 14 d
- Duration:
- 14 d
- Dose descriptor:
- LC50
- Effect conc.:
- > 750 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality
Reference
- Nominal concentrations: 0, 7.5, 37.5, 75, 375 and 750 mg
a.i./kg dw
- Effect data:
Weight: For all concentrations the weight of the worms was
approx. 90-95% of the control.
Mortality: No information given on mortality per test
concentration.
- LC50 > 750 mg a.i./kg dw
Description of key information
The LC50 for soil dwelling organisms is greater than 750 mg/kg soil dw.
Key value for chemical safety assessment
- Short-term EC50 or LC50 for soil macroorganisms:
- 750 mg/kg soil dw
Additional information
One study was found valid without restrictions. In that study performed with Eisenia fetida in artificial soil according to OECD 207 and under GLP no mortality or weight loss was observed (Winkelmann, 2006). Furthermore, two studies were found valid with restrictions. In the study performed by Haque and Ebing (1983) two worm species were tested Eisenia fetida and Lumbricus terrestris L.. For both species 50% effect was not reached. The other study performed by Bouche and Beugnot (1978) was a field study. Two parcels of land (52x36.2 m) were at first exposed to sodium chlorate at a concentration of 200 kg/ha, about two and a half months later a higher concentration of 400 kg/ha was applied. Control parcels were not exposed. One further parcel was simultaneously exposed to chlordane. Six earthworm species were recovered from control treated parcels and the first application did not result in an effect on any of the species found, there was no significant difference found in number and biomass of earthworms per species compared to the control field. An effect was found one week after the second application of 400 kg/ha. The number and biomass of the earthworm populations reduced compared to the control, but within one month complete recovery was shown.
The LC50 for soil dwelling organisms is greater than 750 mg/kg soil dw.
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