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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
Monitoring data
Administrative data
- Endpoint:
- monitoring data
- Type of information:
- other: BUA report
- Adequacy of study:
- other information
- Reliability:
- other: BUA report
- Rationale for reliability incl. deficiencies:
- other: BUA report
Data source
Reference
- Reference Type:
- other: BUA report
- Title:
- Unnamed
- Year:
- 1 990
Materials and methods
- Principles of method if other than guideline:
- BUA report
- 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
Results and discussion
Any other information on results incl. tables
BUA report:
Several publications for monitoring data of 1,2 -dichlorobenzene in the compartments landfill leachate, treated wastewater, sludge, geosphere and biota were summarized in the assessment of the BUA report 53 (1990). The reliability of these publications was not assignable because references were only cited as secondary literature.
Landfill leachate
Leachate from the Georgswerder landfill in Hamburg (Germany) contained total dichlorobenzene levels ranging from non-detectable to 420 µg/l (1981/1982). The sum of the dichlorobenzenes was 450 mg/kg in 1983.
In the USA and Canada, measured concentrations of 15 g/kg and 0.78 µg/l were found. The maximum o-dichlorobenzen concentration in leachate from 44 hazardous landfills in the USA was 670 µg/l.
Treated wastewater
A study of wastewater conducted from 1980 to 1983 in The Netherlands returned o-dichlorobenzene levels of < 5 µg/l in the influents and effluents of six municipal wastewater-treatment plants, five of which also handled industrial wastewater. One sample contained 15 µg/l in the influent and 5 µg/l in the effluent, after treatment in a so-called oxidation ditch.
In the USA and Canada, concentrations of o-dichlorobenzene in influents and effluents (domestic and industrial) ranged from not detectable to 860 µg/l.
Sludge
In the sludge from wastewater treatment plants for municipal and industrial wastewater, the concentrations of o-dichlorobenzene ranged from < 10 µg/kg dry weight to 809 mg/kg dry weight.
Geosphere
Soil from an agricultural area in Germany contained no o-dichlorobenzen (limit of detection: 0.4 mg/kg dry weight). However, soil in and around a domestic refuse dump in The Netherland was contaminated with, among othe rsubstances, up to 325 µg o-dichlorobenzene/kg dry weight.
In the USA, soil contained between 3.5 and 50 mg/kg of o-dichlorobenzene.
Biota:
o-dichlorobenzene was detected in fish (fresh and salt water) at concentrations between "in traces" and 1200 µg/kg, in aquatic (fresh and saltwater) invertebrates between "in traces" and 575 µg/kg, in the fat of pigs at more than 1 µg/kg. Cow's milk containted no (limit of detection: 0.1 µg/kg) or 2.6 µg o-dichlorobenzene/kg (fresh weight) or 81.25 µg/kg (fat), respectively, and the beef contained 1.0 µg/kg (fresh weight) or 47.6 µg/kg (fat), respectively. In the meat and chicken eggs a concentration of 1.8 µg/kg o-dichlorobenzene was measured.
Applicant's summary and conclusion
- Executive summary:
Several publications for monitoring data of 1,2 -dichlorobenzene in the compartments landfill leachate, treated wastewater, sludge, geosphere and biota were summarized in the assessment of the BUA report 53 (1990). The reliability of these publications was not assignable because references were only cited as secondary literature.
Landfill leachate
Leachate from the Georgswerder landfill in Hamburg (Germany) contained total dichlorobenzene levels ranging from non-detectable to 420 µg/l (1981/1982). The sum of the dichlorobenzenes was 450 mg/kg in 1983.
In the USA and Canada, measured concentrations of 15 g/kg and 0.78 µg/l were found. The maximum o-dichlorobenzen concentration in leachate from 44 hazardous landfills in the USA was 670 µg/l.
Treated wastewater
A study of wastewater conducted from 1980 to 1983 in The Netherlands returned o-dichlorobenzene levels of < 5 µg/l in the influents and effluents of six municipal wastewater-treatment plants, five of which also handled industrial wastewater. One sample contained 15 µg/l in the influent and 5 µg/l in the effluent, after treatment in a so-called oxidation ditch.
In the USA and Canada, concentrations of o-dichlorobenzene in influents and effluents (domestic and industrial) ranged from not detectable to 860 µg/l.
Sludge
In the sludge from wastewater treatment plants for municipal and industrial wastewater, the concentrations of o-dichlorobenzene ranged from < 10 µg/kg dry weight to 809 mg/kg dry weight.
Geosphere
Soil from an agricultural area in Germany contained no o-dichlorobenzen (limit of detection: 0.4 mg/kg dry weight). However, soil in and around a domestic refuse dump in The Netherland was contaminated with, among othe rsubstances, up to 325 µg o-dichlorobenzene/kg dry weight.
In the USA, soil contained between 3.5 and 50 mg/kg of o-dichlorobenzene.
Biota:
o-dichlorobenzene was detected in fish (fresh and salt water) at concentrations between "in traces" and 1200 µg/kg, in aquatic (fresh and saltwater) invertebrates between "in traces" and 575 µg/kg, in the fat of pigs at more than 1 µg/kg. Cow's milk containted no (limit of detection: 0.1 µg/kg) or 2.6 µg o-dichlorobenzene/kg (fresh weight) or 81.25 µg/kg (fat), respectively, and the beef contained 1.0 µg/kg (fresh weight) or 47.6 µg/kg (fat), respectively. In the meat and chicken eggs a concentration of 1.8 µg/kg o-dichlorobenzene was measured.
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