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Diss Factsheets
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EC number: 206-019-2 | CAS number: 288-32-4
- 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
Biodegradation in soil
Administrative data
Link to relevant study record(s)
Description of key information
Imidazole biodegrades rapidly in soil.
Key value for chemical safety assessment
- Half-life in soil:
- 2.5 d
- at the temperature of:
- 20 °C
Additional information
The biodegradation potential of imidazole in soil was determined in a study according to OECD guideline 307 and in compliance with GLP criteria (BASF, 2009). In this study, the rate of degradation of 14C radio-labelled imidazole was investigated under aerobic conditions in three soils with ranging ratios of sand, sit and clay, and different pH and organic carbon content. The soils, at portions of 100 g dw and adjusted to 40% of the maximum water holding capacity, were incubated at room temperature in the dark in a batch application at a substance test concentration of 0.4 mg/kg soil dw. The tested concentration was determined to correspond to a field application rate of 150 g/ha (assuming a soil density of 1.5 g/mL and equal distribution in the upper 2.5 cm soil layer). The test vessels were continuously aerated and the exiting air was passed through a system for trapping organic volatiles and 14CO2. Samples were taken after 0, 1, 2, 4, 7, and 10 days. Soil aliquots were extracted 4 times, the extracts measured for radioactivity by liquid scintillation counting (LSC) and then concentrated and subjected to radio-HPLC analysis. The non-extractable residues were determined by combustion and LSC analysis. A total balance of radioactivity in soil was established for each sampling interval and the total mean recoveries for the three soils were in the range from 96.0-99.1% of the total applied radioactivity (TAR). The amount of extractable radioactivity decreased very fast during the study, reaching 0.9-2.5% TAR after 10 days of incubation. The non-extractable residues increased from 6-8% TAR at day 0 to maximum amounts of 14.5-19.0% TAR after 2-4 days and decreased again reaching 6.1-11.5% TAR after 10 days. The mineralization was very high in all three soils reaching 82-91% TAR within 10 days. No other volatile products than CO2 were detected. Overall, imidazole was degraded very rapidly reaching amounts of <3% TAR within 7-10 days in all three soils. The calculated DT50 values ranged from 1.8-2.5 days.
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