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EC number: 204-427-5 | CAS number: 120-80-9
- 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
Biodegradation in soil
Administrative data
- Endpoint:
- biodegradation in soil, other
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- The study is not performed according to an internationally recognized guideline, but is well described, giving interesting insights on the catechol biodegradation in soil.
Data source
Reference
- Reference Type:
- publication
- Title:
- Biodegradation, stabilization in humus, and incorporation into soil biomass od 2,4-D and chlorocatechol carbons
- Author:
- Stott D.E., Martin J.P., Focht D.D., Haider K.
- Year:
- 1 983
- Bibliographic source:
- Soil Sci. Soc. Am. J., 47, 66-70.
Materials and methods
- Principles of method if other than guideline:
- Biodegradation in soil
- GLP compliance:
- not specified
- Test type:
- laboratory
Test material
- Reference substance name:
- Pyrocatechol
- EC Number:
- 204-427-5
- EC Name:
- Pyrocatechol
- Cas Number:
- 120-80-9
- Molecular formula:
- C6H6O2
- IUPAC Name:
- pyrocatechol
- Details on test material:
- The ring 14C-labeled catechol was synthesized according to Martin et al. (1979). The purity was tested by gas chromatography after direct silylation with N-methyl-N-trimethylsilyl-trifluoracetamide.
Constituent 1
- Radiolabelling:
- yes
Study design
- Oxygen conditions:
- aerobic
- Soil classification:
- not specified
- Details on soil characteristics:
- Four soils were used for the tests:
- Steinbeck loam (pH: 5)
- Fallbrook sandy loam (pH: 5.5)
- Greenfield sandy loam (pH: 7)
- Sorrento loam (pH: 7.4)
The four soils used in this study were air-dried, sieved prior to use.
No more information.
Duration of test (contact time)
- Duration:
- 6 mo
Initial test substance concentrationopen allclose all
- Initial conc.:
- 25 ppm
- Based on:
- other: test mat. / Concentration used in both testing periods (6 months and 1 year)
- Initial conc.:
- 500 ppm
- Based on:
- other: test mat. / Concentration used in the 1-year testing period only
- Parameter followed for biodegradation estimation:
- CO2 evolution
Experimental conditions
- Temp.:
- 23 °C
- Humidity:
- other: 60% of the water capacity
- Details on experimental conditions:
- TEST PROCEDURE
- Soils were incubated in the presence of the organic substrates in a closed system. The moisture content was 60% of the water capacity, the temperature was 23°C. The flasks were aerated with a constant stream of humidified and CO2-free air. The amounts of total CO2 and 14C02 released were analysed.
- Concentrations of 25 and 500 ppm were tested for 1 year. Only the concentration of 25 ppm was tested for 6 months.
- Each treatment was duplicated.
PARAMETER FOLLOWED
- The biodegradation of ring labelled catechol, free or linked into model humic acid polymers, was followed over 6-month and 1-year incubation periods, and the distribution of the residual activity in biomass, new humus, and 6N HCl hydrolysable substrates was determined.
- The 14C-labelled catechol was incorporated into model humic acid polymers by reacting about 1 g of a phenolic mixture with 14 mg of peroxidase over a 5-d period.
- The 14C activity of the organic substrates, the 14CO2 evolved during incubation, the residual 14C remaining in the soil after incubation or extractions have been described.
Results and discussion
% Degradation
- % Degr.:
- > 24 - < 50
- Parameter:
- other: dissipation
- Sampling time:
- 6 mo
- Transformation products:
- not specified
- Evaporation of parent compound:
- not specified
- Volatile metabolites:
- not specified
- Residues:
- not specified
- Details on results:
- - 96% of the 14C-labelled catechol in the reactive mixture was recovered in the polymers.
- 37 to 50% of the catechol was lost over 1 year indicating substantial stabilisation of the compound, probably by enzymatic polymerisation reactions. Catechol incorporated into model polymers was still more stable with 6 to 22% of the 14C evolved as CO2.
- After 1 year, about 3 to 8% of the residual 14C activity from catechol was present in the biomass. The amount of residual C in the biomass from the catechol incorporated into the model polymers varied from 0.2 to 2.1%.
- % 14C evolved as 14CO2 in 6 months (catechol at 25 ppm):
in Steinbeck loam: 24
in Fallbrook sandy loam: 50
in Greenfield sandy loam: 28
in Sorrento loam: 26
- % 14C evolved as 14CO2 in 1 year (catechol at 25 ppm):
in Steinbeck loam: 39
in Fallbrook sandy loam: 39
in Greenfield sandy loam: 40
in Sorrento loam: 43
- % 14C evolved as 14CO2 in 1 year (catechol at 500 ppm):
in Steinbeck loam: 50
in Fallbrook sandy loam: 40
in Greenfield sandy loam: 38
in Sorrento loam: 37
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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