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EC number: 202-425-9 | CAS number: 95-50-1
- 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 water and sediment: simulation tests
Administrative data
- Endpoint:
- biodegradation in water: sediment simulation testing
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- significant methodological deficiencies
- Remarks:
- Does not meet important cirteria of today standard methods
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Total reductive dechlorination of chlorobenzenes to benzene by a methanogenic mixed culture enriched from Saale river sediment
- Author:
- Nowak J, Kirsch NH, Hegemann W, Stan HJ
- Year:
- 1 996
- Bibliographic source:
- Appl Microbiol Biotechnol, 45: 700-709
- Reference Type:
- review article or handbook
- Title:
- SIDS Initial Assessment Report For SIAM 13 (Bern, 6 - 9 November 2001) - 1,2-Dichlorobenzene
- Author:
- OECD
- Year:
- 2 001
- Bibliographic source:
- UNEP Publications
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Anoxic sediment samples collected from the Salle river near Jena, Germany, were used as inoculum. This sediment was chosen because of its prior exposure to the waste waters of a pulp mill that used chlorine bleaching. Chlorobenzene-metabolizing methanogenic-enrichment cultures were obtained by inoculating phosphate-buffered RAMM medium with black, anoxic mud (50% v/v) collected form the Saale river and subsequent stationary incubation under strictly anaerobic conditions. Whilst being flushed with nitrogen of the highest purity (6.0), the sediment was transferred and mixed with an equal volume of medium into 1-L serum bottles peviously filled with nitrogen. Several individual chlorobenzene isomers and mixtures of them were added for adaptation (MCB, all DCB, all TCB and 1,2,3,4-tetrachlorobenzene). Upon dechlorination of the added chlorobenzenes, the enrichment cultures were repeatedly fed with the substrates.
The sampling procedure commenced with shaking the bottle for 1 min in order to homogenize the sludge within the aqueous phase. 2 mL homogenate was removed and the liquid extraction of the sample was performed by adding 2 mL aqueous surrogate standard and 2 mL ethyl acetate. The sample was thoroughly shaken and subsequently centrifuged. The supernatant was filtered through a small bed of silica gel and sodium sulfate into an autosampler vial ready for GC analysis. In addition, the gas phases of the bottles were analyed for volatile compounds. - GLP compliance:
- not specified
Test material
- Reference substance name:
- 1,2-dichlorobenzene
- EC Number:
- 202-425-9
- EC Name:
- 1,2-dichlorobenzene
- Cas Number:
- 95-50-1
- Molecular formula:
- C6H4Cl2
- IUPAC Name:
- 1,2-dichlorobenzene
Constituent 1
Study design
- Oxygen conditions:
- anaerobic
- Inoculum or test system:
- natural sediment
Results and discussion
Any other information on results incl. tables
In a study using a methanogenic mixed culture enriched from Saale river sediment, all chlorobenzenes present were transformed by reductive dechlorination via monochlorobenzene to unsubstituted benzene. This occurred after a one week lag phase, which could not be explained. It was found that the dechlorination process was dependent on the biological activity. Reductive dechlorination was stimulated when the mixed cultures were supplemented with pyruvate and methanol.
Applicant's summary and conclusion
- Conclusions:
- In a study using a methanogenic mixed culture enriched from Saale river sediment, all chlorobenzenes present were transformed by reductive dechlorination via monochlorobenzene to unsubstituted benzene.
- Executive summary:
In a study using a methanogenic mixed culture enriched from Saale river sediment, all chlorobenzenes present were transformed by reductive dechlorination via monochlorobenzene to unsubstituted benzene. This occurred after a one week lag phase, which could not be explained. It was found that the dechlorination process was dependent on the biological activity. Reductive dechlorination was stimulated when the mixed cultures were supplemented with pyruvate and methanol.
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