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EC number: - | CAS number: -
- 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
- Study period:
- Jan 18, 2016 - Jun 02, 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 207 (Earthworm, Acute Toxicity Tests)
- GLP compliance:
- yes
- Remarks:
- no OECD GLP
- Analytical monitoring:
- no
- Vehicle:
- yes
- Remarks:
- Acetone
- Details on preparation and application of test substrate:
- A defined artificial soil of the following composition was used for this assay.
Sphagnum peat 10 % (w/w)
Kaolinite clay (Sigma Aldrich) 20 % (w/w)
Silica sand (screened with 0.2 mm sieve) 70 % (w/w)
Based on the results of preliminary test, the test substance was insoluble in water, but could be dissolved in acetone. The test substance was added into the test system by test substance solvent stock solution.
An aliquot solvent solution was separately added to certain amount of silica sand and the solvent was allowed to evaporate off prior to incorporation into formulated artificial soil with deionised reverse osmosis water. These were mixed by mixer to give blank control, solvent control, and 10, 100, and 1000 mg/kg respectively with a nominal moisture content of 40-60 % by mass of the total water-holding capacity with the deionized water. Test medium preparation process of blank control group was the same with other groups, but without organic solvent and test substance. Test medium preparation process of solvent control was the same with other groups, but without test substance. - Test organisms (species):
- Eisenia fetida
- Details on test organisms:
- TEST ORGANISM
- Common name: Eisenia fetida
- Source: Jiang Su province Jurong Stock Farm. (ID: EF-MKT-150915)
- Age at test initiation (mean and range, SD): no data
- Weight at test initiation (mean and range, SD): 572.25 +/- 6.07 mg
ACCLIMATION
- Acclimation period: 14 days
- Acclimation conditions (same as test or not): yes
- Health during acclimation (any mortality observed): no mortality, no other findings - Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 14 d
- Test temperature:
- 20.8 - 21.2 °C
- pH:
- 6.28 & 6.48 (start)
6.28 & 6.45 (end) - Moisture:
- 26.70-29.30 % (start)
26.31-28.93 % (end) - Details on test conditions:
- TEST SYSTEM
- Test container (material, size): 1 L glass vessel, closed
- Amount of soil or substrate: 750 g
- No. of organisms per container (treatment): 10
- No. of replicates per treatment group: 4
- No. of replicates per control: 4
- No. of replicates per vehicle control: 4
OTHER TEST CONDITIONS
- Photoperiod: 24 h/day
- Light intensity: 542 - 589 Lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
day 7 and 14,
VEHICLE CONTROL PERFORMED: yes
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Justification for using less concentrations than requested by guideline:
- Range finding study: 0, 10, 100, 1000 mg/kg dry soil weight
- Test concentrations in definitive study: blank, solvent, 62.5, 125, 250, 500, 1000 mg/kg dry soil weight
- Results used to determine the conditions for the definitive study: range finder results
day 7: 10 % mortality with 1000 mg/kg treatment
day 7: 30 % mortality with 1000 mg/kg treatment - Nominal and measured concentrations:
- 1000 mg/kg soil
- Reference substance (positive control):
- yes
- Remarks:
- Chloroacetamide
- Duration:
- 7 d
- Dose descriptor:
- LC50
- Effect conc.:
- > 1 000 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Key result
- Duration:
- 14 d
- Dose descriptor:
- LD50
- Effect conc.:
- > 1 000 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- The mortalities of the earthworm in the blank control group and solvent control group were 2.5 % and 0 % respectively, which were not more than 10 %, so the test was valid.
The mortalities of the treatment group with the nominal concentration of 1000 mg/kg dry artificial soil weight after 7 and 14 days were 7.5 % and 12.5 % respectively. Under condition of the test, the 7-Day LC50 and the 14-Day LC50 for the test substance to earthworms (Eisenia fetida) based on the nominal test concentrations were both higher than 1000 mg/kg dry soil weight. - Results with reference substance (positive control):
- LD50 at about 15 mg/kg soil dw
- Reported statistics and error estimates:
- Standard statistical methods have been applied for data processing.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Under conditions of the test, the 7 -day LD50 and the 14 -day LD50 for the test substance to earthworms (Eisenia fetida) based on nominal test concentrations were higher than 1000 mg/kg dry soil weight.
- Executive summary:
In this study, the acute toxicity of the test substance to Eisenia fetida was determined in a 14 days artificial soil test. The study design followed the "OECD, Guidelines for the Testing of Chemicals, 1984, 207 Earthworm, Acute Toxicity Test".
Based on the results of range-finding test, five treatment groups, one blank control group and one solvent control group which had four replicates of 10 worms per concentration were included in definitive test. The nominal concentrations of the treatment groups were 62.5, 125, 250, 500 and 1000 mg/kg dry artificial soil weight. The number of mortalities were determined after 7 and 14 days exposure.
The mortalities of the earthworm in the blank control group and solvent control group were 2.5 % and 0 % respectively, which were not more than 10 %, so the test was valid. The mortalities of the treatment group with the nominal concentration of 1000 mg/kg dry artificial soil weight after 7 and 14days were 7.5 % and 12.5 % respectively. Under condition of the test, the 7-Day LC50 and the 14-Day LC50 for the test substance to earthworms (Eisenia fetida) based on the nominal test concentrations were both higher than 1000 mg/kg dry soil weight.
Reference
Description of key information
Under condition of the test, the 7-Day LC50 and the 14-Day LC50 for the test substance to earthworms (Eisenia fetida) based on the nominal test concentrations were both higher than 1000 mg/kg dry soil weight.
Key value for chemical safety assessment
- Short-term EC50 or LC50 for soil macroorganisms:
- 1 000 mg/kg soil dw
Additional information
In this study, the acute toxicity of the test substance to Eisenia fetida was determined in a 14 days artificial soil test. The study design followed the "OECD, Guidelines for the Testing of Chemicals, 1984, 207 Earthworm, Acute Toxicity Test".
Based on the results of range-finding test, five treatment groups, one blank control group and one solvent control group which had four replicates of 10 worms per concentration were included in definitive test. The nominal concentrations of the treatment groups were 62.5, 125, 250, 500 and 1000 mg/kg dry artificial soil weight. The number of mortalities were determined after 7 and 14 days exposure.
The mortalities of the earthworm in the blank control group and solvent control group were 2.5 % and 0 % respectively, which were not more than 10 %, so the test was valid. The mortalities of the treatment group with the nominal concentration of 1000 mg/kg dry artificial soil weight after 7 and 14days were 7.5 % and 12.5 % respectively. Under condition of the test, the 7-Day LC50 and the 14-Day LC50 for the test substance to earthworms (Eisenia fetida) based on the nominal test concentrations were both higher than 1000 mg/kg dry soil weight.
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