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Diss Factsheets
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EC number: 200-315-5 | CAS number: 57-13-6
- 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
Bioaccumulation: terrestrial
Administrative data
- Endpoint:
- bioaccumulation: terrestrial
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model, but not (completely) falling into its applicability domain, and documentation / justification is limited
Data source
Reference
- Reference Type:
- publication
- Title:
- BIOACCUMULATION IN THE SOIL TO EARTHWORM SYSTEM
- Author:
- Des W. CONNELL and Ross D. MARKWELL
- Year:
- 1 990
- Bibliographic source:
- Chemosphere, Vol. 20, Nos. 1-2, pp. 91-100, 1990
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 317 (Bioaccumulation in Terrestrial Oligochaetes)
- GLP compliance:
- no
Test material
- Reference substance name:
- Urea
- EC Number:
- 200-315-5
- EC Name:
- Urea
- Cas Number:
- 57-13-6
- Molecular formula:
- CH4N2O
- IUPAC Name:
- urea
- Details on test material:
- It is assumed that the purity is 100%
Constituent 1
Results and discussion
Any other information on results incl. tables
The sources of variation in this study are substantial. Several sources of data from experiments conducted under different conditions are included. Also, it has been demonstrated (Chessels et. al., 1988) that pesticides in soils establish concentration patterns and gradients due to varying environmental conditions, leading to irregular exposure. Despite these limitations, the data are broadly consistent with the transfer of lipophilic compounds through a three phase system involving soil to soil water to organism partitioning, analogous to that observed in oligochaete worms. This is a passive process and is principally dependent on the lipid content of the worms and the organic carbon content of the soil. Transfer from soil to soil water can be described by the same relationships established for sediment to water equilibria. The transfer from soil water to earthworm is described by:
log Kb = log Kow - 0.6
This relationship is consistent with the theoretically derived equation for bioconcentration, which has been found to apply to bioconcentration by aquatic organisms. The bioaccumulation factor derived from the three phase partition theory is in accord with the observed bioaccumulation factor. It demonstrates a weak dependence on the log Kow value and strong dependence on the lipid content of the organism and the organic matter content of the soil.
The Log Kow for urea is -1.73.
Hence the log Kb as calculated with the equation above is -2 .23.
This indicates a low potential for bioaccumulation of urea.
Applicant's summary and conclusion
- Conclusions:
- Low potential for bioaccumulation.
- Executive summary:
The sources of variation in this study are substantial. Several sources of data from experiments conducted under different conditions are included. Also, it has been demonstrated (Chessels et. al., 1988) that pesticides in soils establish concentration patterns and gradients due to varying environmental conditions, leading to irregular exposure. Despite these limitations, the data are broadly consistent with the transfer of lipophilic compounds through a three phase system involving soil to soil water to organism partitioning, analogous to that observed in oligochaete worms. This is a passive process and is principally dependent on the lipid content of the worms and the organic carbon content of the soil. Transfer from soil to soil water can be described by the same relationships established for sediment to water equilibria. The transfer from soil water to earthworm is described by:
log Kb = log Kow - 0.6
This relationship is consistent with the theoretically derived equation for bioconcentration, which has been found to apply to bioconcentration by aquatic organisms. The bioaccumulation factor derived from the three phase partition theory is in accord with the observed bioaccumulation factor. It demonstrates a weak dependence on the log Kow value and strong dependence on the lipid content of the organism and the organic matter content of the soil.
The Log Kow for urea is -1.73.
Hence the log Kb as calculated with the equation above is -2 .23.
This indicates a low potential for bioaccumulation of urea.
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