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EC number: 228-055-8 | CAS number: 6104-30-9
- 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: long-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- No data relating to untreated controls were provided. Study was assessed with a reliability of two in OECD SIDS urea and in contrast, with a reliability of four in OECD SIDS of this substance. The observed effects were attributed to the lowering of pH observed in parallel with IBDU application in the absence of liming. Since this study provides evidence on the harmfullness of IBDU in long term treatments among 20 years, we believe it can be considered for covering the endpoint of long term toxicity to soil macroorganisms.
- Principles of method if other than guideline:
- other: field test
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Lumbricus sp.
- Animal group:
- annelids
- Study type:
- field study
- Substrate type:
- natural soil
- Remarks:
- 20 years
- Key result
- Duration:
- 365 d
- Dose descriptor:
- other: EC
- Effect conc.:
- 216 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: biomass and number of earthworms
- Endpoint:
- toxicity to soil macroorganisms except arthropods: short-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 207 (Earthworm, Acute Toxicity Tests)
- Version / remarks:
- 1984
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Details on preparation and application of test substrate:
- - Method of mixing into soil (if used): The test substance was pulverized in a mortar before weight in.
The test substance was weight in and added direct to each parallel (10 g quartz sand). Afterwards these
10 g quartz sand were mixed with 740 g of the substrate and 250 ml dernineralized water was added to
adjust the water content at 33 ± 2% of dry weight.
- Controls: yes - Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- TEST ORGANISM
- Common name: earthworm
- Source: supplier (Mrs . Haber from 64367 Mahltal-
Frankenhausen)
- Age at test initiation (mean and range, SD): adult, 9 months
- Weight at test initiation (mean and range, SD): 300-600 mg
ACCLIMATION
- Acclimation conditions (same as test or not): Before being used in the test, the animals were kept in boxes and fed with horse
manure.
- Adaptation: 24 h before the test, in test substrate without test substance - Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 14 d
- Test temperature:
- 19.1°C-22.1°C
- pH:
- 5.8 (at day 0)
- Moisture:
- 33.1-33.3%
- Details on test conditions:
- see below: Any other information on materials and methods incl. tables
- Nominal and measured concentrations:
- Nominal concentrations: 125, 250, 500, 1000 mg/kg and control
- Reference substance (positive control):
- yes
- Remarks:
- chloracetamide
- Duration:
- 14 d
- Dose descriptor:
- LC0
- Effect conc.:
- 250 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 14 d
- Dose descriptor:
- LC100
- 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:
- LC50
- Effect conc.:
- 648 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Key result
- Duration:
- 14 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 250 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Key result
- Duration:
- 14 d
- Dose descriptor:
- LOEC
- Effect conc.:
- 500 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- see below
- Results with reference substance (positive control):
- - Results with reference substance valid? yes
- Relevant effect levels: LC50 (14d) = 16.7 mg/kg - Validity criteria fulfilled:
- yes
Referenceopen allclose all
Effects of fertilizers on lumbricid earthworms in uncultivated turfgrass on loamy sand soil were related to their effects on soil acidity. IBDU had effects on earthworm numbers and biomass and lowered pH dose-dependently by 1 to 1.5 units. Endogaeic species of earthworms such as Aporrectodea spp. were more strongly affected than the epigaeic group of Lumbricus spp., although an exception was noted for A. caliginosa tuberculata. Strongly acidified soils contained more organic matter than soils which were less acidified, accumulations of soil organic matter were associated with accumulations of surface thatch. The study indicates that the application of fertilizers to grasslands for long periods may have a deleterious effect on earthworms in the absence of liming, as the effects were related to changes in soil acidity.
In summary, this study revealed that, IBDU (2 applications per year of 180 kg N/ha = 216 mg IBDU/kg soil) had effects on earthworm numbers and biomass.
LC50 (14 d): 648 (95% confidence limits 587-716) mg/kg
LC50 (7 d): 648 (95% confidence limits 591-712) mg/kg.
No particular behavioural or morphological changes were observed.
Description of key information
Acute toxicity to earthworm: LC50 (14d): 648 mg/kg soil d.w.
Key value for chemical safety assessment
Additional information
Acute toxicity to Eisenia fetida was tested in a study according to OECD guideline 207. The 14d- LC50 value was 648 mg/kg soil (BASF AG 2001). Ma et al. (1990) studied long-term effects (20 y) on nitrogenous fertilizers usage on lumbricid earthworms in soil. This study revealed that, IBDU (2 applications per year of 180 kg N/ha = 216 mg IBDU/kg soil) had effects on earthworm numbers and biomass. However, the effects were attributed to the lowering of pH observed in parallel with IBDU application in the absence of liming.
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