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EC number: 202-045-3 | CAS number: 91-16-7
- 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:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Test system is well described and controls show it functions well.
Data source
Reference
- Reference Type:
- publication
- Title:
- Effect of aromatic compounds, humic acids and lignins on growth of the earthworm Eisenia foetida
- Author:
- Roy Hartenstein
- Year:
- 1 982
- Bibliographic source:
- Soil biology and biochemistry 14, pp.595-599
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Test substance was added in varying concentrations to sludge. Sludge was placed on silt loam in a petri dish and worms were added. Survival and growth were checked over 6 weeks.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Veratrole
- EC Number:
- 202-045-3
- EC Name:
- Veratrole
- Cas Number:
- 91-16-7
- Molecular formula:
- C8H10O2
- IUPAC Name:
- 1,2-dimethoxybenzene
- Test material form:
- other: liquid
- Details on test material:
- Chemicals obtained from Aldrich Chemical Company, Milwaukee, Wisconsin, used without further purification
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
Test substrate
- Vehicle:
- no
- Details on preparation and application of test substrate:
- - Method of application to soil surface: Test substances were processed for assay by mixing the required amount into 100 g sludge which contained 11-15% solids. Assuming exactly 13% solids in sludge the concentrations were 0.1 to 8% (w/w) dry weight.
About 30 g spiked sludge (average 13% solids) was placed over a 4 mm depth of silt loam in a 20x100 mm petri dish.
Test organisms
- Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- Stock cultures maintained on horse manure or activated sludge. 2 hatchlings each under 10 mg live weight were added to Petri dishes.
Study design
- Study type:
- laboratory study
- Substrate type:
- other: silt loam
- Limit test:
- no
- Total exposure duration:
- 6 wk
- Remarks:
- Measurements after 2, 4 and 6 weeks
- Post exposure observation period:
- No post-exposure period
Test conditions
- Test temperature:
- 24 +/- 1 degrees Celsius
- pH:
- no data
- Moisture:
- No exact data. Sludge contained 11 to 15% of solids, placed on silt loam layer.
- Details on test conditions:
- Growth was determined at 2, 4 and 6 weeks by rinsing the worms in distilled water, blotting and weighing. Worms were transferred to freshly prepared substance after 4 weeks.
- Nominal and measured concentrations:
- Substances tested at 0, 0.1, 1, 4 and 8 % (w/w) dry weight,
5 replicates each - Reference substance (positive control):
- not specified
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 6 wk
- Dose descriptor:
- LC100
- Effect conc.:
- 0.1 other: % (w/w)
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 6 wk
- Dose descriptor:
- other: significant growth reduction
- Effect conc.:
- < 0.1 other: % (w/w)
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth
- Remarks:
- After 6 weeks at 0.1 % mortality was 100%. This was the lowest test concentration
- Details on results:
- Hatchlings in control dishes would gain more than 500 mg in 6 weeks. An average weight of 582 mg +/- 85 SD, with a c.v. of 14.6% was attained by controls in 6 weeks in 45 similar assays during 16 months. This reflects both variation in earthworm growth and sludge quality. Mortality in controls was less than 2%.
Dimethoxybenzenes were severely more toxic than di- and trihydroxybenzenes and monosubstituted hydroxybenzenes - Results with reference substance (positive control):
- no data
- Reported statistics and error estimates:
- Significant differences for growth reduction were detected by the Neuman-Keul test (Zar 1974) (but not relevant for this test substance due to 100 % mortality). Mortality was said to be significant if 5 or more earthworms died.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not applicable
- Remarks:
- mortality in control very low, and high growth make test reliable
- Conclusions:
- 100% mortality of the test organism Eisenia fetida was observed at the lowest test concentration of 0.1 % (w/w in sludge) in a mixture of active sludge and soil.
- Executive summary:
Eisenia fetida was tested in spiked activated sludge with concentrations from 0.1 to 8% (w/w) dry wt, including controls. The test duration was 6 weeks. Blank control performance of the test was good. For the test substance, 100 % mortality was observed at the lowest test concentration of 0.1 % (w/w in sludge dry weight) in a mixture of activated sludge and soil.
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