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EC number: 939-478-9 | 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:
- 07 Dec 2015 - 08 Jan 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: The Guidelines for Testing of Chemicals - Effects on Biotic Systems
- Version / remarks:
- 2013
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: SEPA 2004, HJ/T 153-2004, the guidelines for the testing of chemicals.
- Version / remarks:
- 2004
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 207 (Earthworm, Acute Toxicity Tests)
- Version / remarks:
- 1984
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on preparation and application of test substrate:
- - Method of preparation of test substrate: Direct additions into the soil. A total amount of 10 g mixture of the test substance and quartz sand was prepared firstly and then mixed with 550 g dry weight of soil for each test container. The medium was thoroughly mixed and deionised water was added finally to give an overall moisture content of about 35 per cent of the dry weight. Moisture content was determined by weighing and then drying a small sample at 105 °C and re-weighing.
- Controls: yes, blank control - Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- TEST ORGANISM
- Common name: earthworm
- Source: Nanjing Earthworm Nursery, Nanjing, China
- Age at test initiation: adult (two months old with clitellum)
- Weight at test initiation: 376 - 416 mg
ACCLIMATION
- Quarantaine period: Earthworms newly obtained in the lab were released from quarantine after 14 days and then this batch was pre-cultured in soil with cow dung for 272 days (Batch No.: E20150327E).
- Acclimation period: Before the test, the worms were acclimated in test soil for another 24 h. The worms were then washed quickly with distilled water and surplus water absorbed on filter paper before use. - Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- yes
- Total exposure duration:
- 14 d
- Test temperature:
- 19.8 - 20.3 °C
- pH:
- Start: 6.14 - 6.33
End: 6.17 - 6.36 - Moisture:
- Moisture of soil at start: 35%
Moisture of soil at end: 27 - 30%
Air humidity: 78 - 82% - Details on test conditions:
- TEST SYSTEM
- Test container: 1L glass spoutless beakers, 12 cm diameter, covered with plastic films with small ventilation holes
- Amount of soil or substrate: 560 g (dry weight)
- No. of organisms per container (treatment): 10
- No. of replicates per treatment group: 4
- No. of replicates per control: 4
SOURCE AND PROPERTIES OF SUBSTRATE
- Composition (artificial substrate): 10% Sphagnum peat (pH 6.0, no visible plant remains, finely ground, dried), 20% kaolin clay (kaolinite content preferably above 30%), 70% quartz sand (fine sand should be dominant with 80% of the particles between 50 and 200 microns).
- Moisture content: 35% dry soil weight.
- Preparation: The dry constituents were blended in the correct proportions and mixed thoroughly with a large-scale laboratory mixer.
OTHER TEST CONDITIONS
- Photoperiod: the vessels were covered were plastic films and kept under continuous illumination
- Light intensity: 400 - 800 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : mortality at day 7 and at day 14.
- Other measurements: pH and moisture content at day 0 and at day 14.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: not applicable since the test was performed as a limit test.
- Range finding study test concentrations: 100, 500 and 1000 mg/kg dw
- Results used to determine the conditions for the definitive study: yes, based on the results of the range finding study, a limit test was carried out using a nominal concentration of 1000 mg/kg (dry weight of soil) - Nominal and measured concentrations:
- Nominal concentration: 1000 mg/kg dry soil
- Reference substance (positive control):
- yes
- Remarks:
- 2-Chloracetamide (performed three times a year; most recent test presented in report)
- Key result
- Duration:
- 14 d
- Dose descriptor:
- LC50
- Effect conc.:
- > 1 000 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- - Mortality at end of exposure period: no mortality occured at the blank control group and at the limit concentration.
- Average weight at the end of exposure: 318 - 353 mg
- Behavioural effects: at the beginning of the administration, test worms soon disappeared into the test soil medium. During the test, all earthworms remained in the soil.
- No unusual circumstances that might have affected the integrity and quality of the study were observed. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Relevant effect levels: 14 d LC50: 21.2 mg/kg dry soil, 95% confidence limit 16.9 - 26.6 mg/kg dry soil. - Reported statistics and error estimates:
- none
- Validity criteria fulfilled:
- yes
- Remarks:
- No mortality occured in the control groups.
- Conclusions:
- The LC50 for acute toxicity to earthworms (14-day exposure) was > 1000 mg/kg (dry soil). The highest concentration causing no mortality at 14 days was 1000 mg/kg (dry soil)
- Executive summary:
In an acute toxicity test, performed according to "Guideline HJ/T 153 -2004" and "Guidelines for the Testing of Chemicals-Effects on Biotic Systems", with reference to OECD guideline 207, and according to GLP principles, Eisenia fetida (earthworm) were exposed to a limit concentration (1000 mg/kg (dry soil)) of the test substance for 14 days. A blank control group was included. The treatment group and the control groups consisted of 4 replicates of 10 worms each. The test was performed in artificial soil consisting of sphagnum peat (10%), kaolin clay (20%) and quartz sand (70%). Based on the results of a range finding study in which no mortality occured in all tested concentrations (10, 500 and 1000 mg/kg dry soil), a nominal concentration of 1000 mg/kg dry soil was used in the limit test. Mortality was recorded at day 7 and at day 14. No mortality occured in the blank control group and in the treatment group. The LC50 was determined to be >1000 mg/kg (dry soil), based on the nominal test concentration. The test is considered reliable without restriction.
Reference
Table 1: Number of Dead Earthworms in the Limit Test
Concentration applied to soil (mg/kg (dry soil)) |
Number of the test worms |
Number the dead |
|
7 d |
14 d |
||
0 |
10 |
0 |
0 |
0 |
10 |
0 |
0 |
0 |
10 |
0 |
0 |
0 |
10 |
0 |
0 |
1000 |
10 |
0 |
0 |
1000 |
10 |
0 |
0 |
1000 |
10 |
0 |
0 |
1000 |
10 |
0 |
0 |
LC50 (mg/kg (dry soil)) |
>1000 |
>1000 |
Description of key information
In an acute toxicity test, performed according to "Guideline HJ/T 153 -2004" and "Guidelines for the Testing of Chemicals-Effects on Biotic Systems", with reference to OECD guideline 207, and according to GLP principles, Eisenia fetida (earthworm) were exposed to a limit concentration (1000 mg/kg (dry soil)) of the test substance for 14 days. A blank control group was included. The treatment group and the control groups consisted of 4 replicates of 10 worms each. The test was performed in artificial soil consisting of sphagnum peat (10%), kaolin clay (20%) and quartz sand (70%). Based on the results of a range finding study in which no mortality occurred in all tested concentrations (10, 500 and 1000 mg/kg dry soil), a nominal concentration of 1000 mg/kg dry soil was used in the limit test. Mortality was recorded at day 7 and at day 14. No mortality occurred in the blank control group and in the treatment group. The LC50 was determined to be >1000 mg/kg (dry soil), based on the nominal test concentration. The test is considered reliable without restriction.
Key value for chemical safety assessment
Additional information
14d-LC50 > 1000 mg/kg, no acute hazard identified.
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