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EC number: - | 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

Biodegradation in soil
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in soil: simulation testing
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- 1994
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study without detailed documentation
- Justification for type of information:
- Refer to the Quaternary ammonium salts (QAS) category or section 13 of IUCLID for details on the category justification. The study with the read across substance is considered sufficient to fulfil the information requirements as further explained in the provided endpoint summary.
- Reason / purpose for cross-reference:
- read-across source
- Principles of method if other than guideline:
- The study comprised two treatments - test substance and chemical blank control, each with three replicates - and was carried out in biometers containing approximately 50 g dry weight equivalents of soil. The test substance was added in appropriate amounts of deionised water not exceeding that required for bringing the soils to 50 to 70% of the maximum moisture capacity. The amount of water to remoisturize 50 g of soil to approximately 60% of its maximum field capacity was determined from the data of the moisture content of the soil after air-drying and the maximum field moisture capacity. The soils were maintained at this moisture level by the addition of deionised water, when necessary. Loam was added to the biometers after the test solutions to facilitate moistening of the soils uniformly by capillary action. Test substance was added at a concentration of 10 mg carbon per 50 g soil. The side tube of the biometer contained 20 mL 0.2 M KOH for absorbing carbon dioxide produced by the microorganisms. The test was incubated at 22 ± 3°C and run for approximately 90 d. The theoretical CO2 production of the test substance was calculated from its carbon content. The amounts of carbon dioxide produced was calculated by subtracting the mean carbon dioxide production in the test systems containing the test substance and the mean carbon dioxide production level in the control blank. Biodegradation was calculated as the ratio of experimental carbon dioxide production to theoretical carbon dioxide production [ThCO2P].
- GLP compliance:
- no
- Test type:
- laboratory
- Oxygen conditions:
- aerobic
- Soil classification:
- other: loam
- Key result
- % Degr.:
- 64
- Parameter:
- CO2 evolution
- Sampling time:
- 70 d
- Key result
- DT50:
- 40 d
- Remarks on result:
- other: DT50
- Transformation products:
- no
- Details on results:
- The test substance was biodegraded in loam. The percentage reached at Day 70 was 64. This percentage of the theoretical carbon dioxide production presumes complete mineralisation. The DT50 was estimated to be 40d.
- Conclusions:
- Based on the results of the study, the test substance was 64% biodegraded in loam at Day 70. This percentage of the theoretical carbon dioxide production presumes complete mineralisation. The DT50 was estimated to be 40 days.
- Executive summary:
A study was conducted to determine the biodegradation of the read across substance, C12-16 ADBAC, in a loamy soil. The study comprised two treatments - test substance and chemical blank control, each with three replicates - and was carried out in biometers containing approximately 50 g dry weight equivalents of soil. The test substance was added in appropriate amounts of deionised water not exceeding that required for bringing the soils to 50 to 70% of the maximum moisture capacity. The soils were maintained at this moisture level by the addition of deionised water, when necessary. Loam was added to the biometers after the test solutions to facilitate uniform moistening of the soils by capillary action. Test substance was added at a concentration of 10 mg carbon per 50 g soil. The side tube of the biometer contained 20 mL 0.2 M KOH for absorbing carbon dioxide produced by the microorganisms. The test was incubated at 22 ± 3°C and run for approximately 90 d. The theoretical CO2 production of the test substance was calculated from its carbon content. The amount of carbon dioxide produced was calculated by subtracting the mean carbon dioxide production in the test systems containing the test substance and the mean carbon dioxide production level in the control blank. Biodegradation was calculated as the ratio of experimental carbon dioxide production to theoretical carbon dioxide production [ThCO2P]. Based on the results of the study, the test substance was 64% biodegraded in loam at Day 70. This percentage of the theoretical carbon dioxide production presumes complete mineralisation. The DT50 was estimated to be 40 days (van Ginkel, 1994). Based on the results of the read across study, the test substance, C12-14 TMAC, can also be expected to undergo 64% biodegradation in loam at Day 70, with DT50 of 40 days.
Reference
Description of key information
Based on the results of the read across study, th test substance, C12-14 TMAC, is considered to undergo around 64% biodegraded in a loam soil with an estimated DT50 of 40 days.
Key value for chemical safety assessment
- Half-life in soil:
- 40 d
- at the temperature of:
- 22 °C
Additional information
A study was conducted to determine the biodegradation of the read across substance, C12-16 ADBAC, in a loamy soil. The study comprised two treatments - test substance and chemical blank control, each with three replicates - and was carried out in biometers containing approximately 50 g dry weight equivalents of soil. The test substance was added in appropriate amounts of deionised water not exceeding that required for bringing the soils to 50 to 70% of the maximum moisture capacity. The soils were maintained at this moisture level by the addition of deionised water, when necessary. Loam was added to the biometers after the test solutions to facilitate uniform moistening of the soils by capillary action. Test substance was added at a concentration of 10 mg carbon per 50 g soil. The side tube of the biometer contained 20 mL 0.2 M KOH for absorbing carbon dioxide produced by the microorganisms. The test was incubated at 22 ± 3°C and run for approximately 90 d. The theoretical CO2 production of the test substance was calculated from its carbon content. The amount of carbon dioxide produced was calculated by subtracting the mean carbon dioxide production in the test systems containing the test substance and the mean carbon dioxide production level in the control blank. Biodegradation was calculated as the ratio of experimental carbon dioxide production to theoretical carbon dioxide production [ThCO2P]. Based on the results of the study, the test substance was 64% biodegraded in loam at Day 70. This percentage of the theoretical carbon dioxide production presumes complete mineralisation. The DT50 was estimated to be 40 days (van Ginkel, 1994). Based on the results of the read across study, the test substance, C12-14 TMAC, can also be expected to undergo 64% biodegradation in loam at Day 70, with DT50 of 40 days.
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