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EC number: 931-334-3 | 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
- Endpoint:
- toxicity to soil macroorganisms except arthropods: long-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 5/2/2013 - 29/4/2013
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Study according to international guideline (OECD guideline 222) under GLP. No deviations from guideline reported. The study was assigned a Klimisch 2 rating due to the read-across purpose, in accordance with the ECHA Practical guide #6 on the reporting of read-across in IUCLID.
Cross-reference
- Reason / purpose for cross-reference:
- read-across: supporting information
Reference
As the test substance does not solve in water, the mechanism of partitioning from the water phase and thus uptake by diffusion from the water phase does not take place. Thus exposure of terrestrial organisms to the test substance may occur only by oral intake of solid particles of the test substance. An effect in the organism would then be caused by internal partitioning of test substance (as modelled by equilibrium partitioning and for highly lipophilic substance with an additional factor of 10, see Guidance Document on Information Requirements and Chemical Safety Assessment R.10 and R.16). However, for activated carbon no absorption is expected (see toxicokinetic assessment). The absence of effects from oral intake of activated carbon is supported by the results of an acute toxicity study with rats where no adverse effects were observed after oral exposure to 2000 mg/kg (C80453). To demonstrate the absence of effects in terrestrial organisms, a reproduction toxicity test with earthworms (OECD 222) was performed with Activated Carbon - High Density Skeleton. This study was read across to Activated Caron- Low Density Skeleton in this dossier. The NOEC in this study was observed to be 1000 mg/kg soil. Therefore further testing with terrestrial organisms is waived.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 222 (Earthworm Reproduction Test (Eisenia fetida/Eisenia andrei))
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- ISO 11268-2 (Effects of Pollutants on Earthworms. 2. Determination of Effects on Reproduction)
- Deviations:
- no
- Principles of method if other than guideline:
- not relevant
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Activated carbon powder (coconut based)
- IUPAC Name:
- Activated carbon powder (coconut based)
- Test material form:
- solid: particulate/powder
- Details on test material:
- - Name of test material (as cited in study report): Activated carbon powder (coconut based)
- Substance type: Black powder
- Physical state: solid
- Storage condition of test material: At room temperature (20 ± 5 °C), under dark and dry conditions
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not relevant
Sampling and analysis
- Analytical monitoring:
- no
- Details on sampling:
- not relevant
Test substrate
- Vehicle:
- no
- Details on preparation and application of test substrate:
- - Method of mixing into soil:Activated carbon powder (coconut based) was weighed separately for each concentration using an analytical balance and fine quartz sand was added until a final net weight of 20 g was reached. After mixing with a spoon to reach a homogeneous distribution of the test item within the sand the mixture was added to artificial soil equivalent to 2030 g dry weight. While mixing the artificial soil in a laboratory mixer for approximately 5 min the soil of each treatment group was moistened with deionised water. Each group was treated in one batch (two in the control) which was then split into the replicates.
- Controls: Untreated soil (same amount of untreated quartz sand as in the test item groups and moistened with deionised water)
Test organisms
- Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- TEST ORGANISM
- Common name: Eisenia fetida (Savigny 1826)
- Source: Bred under standardised conditions in IBACON laboratories
- Age at test initiation: Adults, Approximately 12 months, with well-developed clitellum, age range between test individuals not differing by more than 4 weeks
- Weight at test initiation: 300 mg to 600 mg
ACCLIMATION
- Acclimation period: 1 day, in artificial soil, under test conditions
- Acclimation conditions: same as test conditions
Study design
- Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 8 wk
- Post exposure observation period:
- After 4 weeks, adult worms were counted, removed and weighed per replicate after being washed under tap water and dried on paper towels. Missing earthworms and earthworms that failed to respond to gentle stimulation were considered to be dead. The remaining soil (without the adult worms) was then returned to the respective test containers. Exposure Time of Offspring: Additional 28 days after removal of the adult worms.
Test conditions
- Test temperature:
- 18-22 ºC
- pH:
- 6.0 ± 0.5
- Moisture:
- At experimental start: 18.9% to 19.2% (52.5% to 53.4% of the maximum water holding capacity)
At experimental end: 19.5% to 22.3% (54.2% to 61.9% of the maximum water holding capacity) - Details on test conditions:
- TEST SYSTEM
- Test container: Plastic boxes (18.3 cm x 13.6 cm x 6 cm, tapered towards the bottom, with a soil surface of approximately 16.5 cm x 11.5 cm = 189.75 cm²) with perforated transparent lids to enable exchange of air, to minimise evaporation from the artificial soil, and to prevent the worms from escaping.
- Amount of soil or substrate: Each container was filled with 598.6 g of the prepared soil (500 g dry weight plus deionised water plus 5 g food). The height of the soil layer in the containers was approximately 4 - 5 cm.
- No. of organisms per container (treatment): 10
- No. of replicates per treatment group: 4
- No. of replicates per control: 8
SOURCE AND PROPERTIES OF SUBSTRATE
- Composition (artificial substrate): Based on OECD 222 but with reduced organic matter content:
• 5% Sphagnum-peat, air-dried and finely ground (2 mm); (Floragard, Vertriebs GmbH für Gartenbau, 26138 Oldenburg, Germany)
• 20% Kaolin clay (Erbslöh, 65558 Lohrheim, Germany)
• 74.8% fine quartz-sand (F34) containing more than 50% by mass of particle size 0.05 mm to 0.2 mm; (Quarzwerke Frechen, Postfach 1780, 50207 Frechen, Germany)
Calcium carbonate (CaCO3) was added to adjust pH to 6.0 ± 0.5 (Merck, 64293 Darmstadt, Germany).
The artificial soil was moistened to approximately half of the final water content 1 day before the application. The additional water required to achieve the final water content was added when applying the test item.
- Maximum water holding capacity:36% of the dry weight
OTHER TEST CONDITIONS
- Photoperiod: 16 h light : 8 h dark
- Light intensity: Within the range of 400 lux to 800 lux
EFFECT PARAMETERS MEASURED :
- Number of dead adult earthworms at day 28 after application (including any missing ones)
- Number of affected adult earthworms (e.g. lack of movement, rigidity, etc) at day 28 after application
- Body weights were determined at start (day 0) and 28 days after application
- Number of juveniles 56 days after introduction of the test animals
After 4 weeks, adult worms were counted, removed and weighed per replicate after being washed under tap water and dried on paper towels.
The remaining soil (without the adult worms) was then returned to the respective test containers. Exposure Time of Offspring: Additional 28 days after removal of the adult worms.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 3.2
- Range finding study: no - Nominal and measured concentrations:
- nominal: 31.6, 100.0, 316.0, 1000.0, 3200 mg/kg soil
- Reference substance (positive control):
- yes
- Remarks:
- Carbendazim
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 4 wk
- Dose descriptor:
- NOEC
- Effect conc.:
- 3 200 other: mg/kg soil
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Key result
- Duration:
- 4 wk
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 000 other: mg/kg soil
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: weight
- Key result
- Duration:
- 8 wk
- Dose descriptor:
- NOEC
- Effect conc.:
- 3 200 other: mg/kg soil
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Details on results:
- - Mortality at end of exposure period (28 d): 0%
- Results with reference substance (positive control):
- - Results with reference substance valid
- Relevant effect levels: EC50 1.7 mg/kg soil - Reported statistics and error estimates:
- Standard procedures, Williams t-test (weight changes) and Bonferroni-Welch t-test (reproduction).
Any other information on results incl. tables
Validation criteria were met: Control mortality was 0%. The number of juvenile worms per replicate was 185 to 312. The coefficient of Variance of Reproduction in Control was 21.5%.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- All study validity criteria were met
- Conclusions:
- In an earthworm reproduction and growth study with Activated carbon powder (coconut based) the No Observed Effect Concentration (NOEC) for growth, reproduction and feeding activity of the earthworm Eisenia fetida was determined to be 1000 mg test item/kg soil.
- Executive summary:
In an earthworm reproduction and growth study according to OECD guideline 222 with Activated carbon powder (coconut based) the No Observed Effect Concentration (NOEC) for growth, reproduction and feeding activity of the earthworm Eisenia fetida was determined to be 1000 mg test item/kg soil.
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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