Registration Dossier
Registration Dossier
Diss Factsheets
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EC number: 201-247-9 | CAS number: 80-07-9
- 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

Endpoint summary
Administrative data
Description of key information
Additional information
Environmental levels
Air:
The concentrations reported are 0.3 to 0.05 ng/m³ in the air (Arnér et al 2004).
Soil & Sediments
Soils:
No MEC available
Freshwater lake sediments:
MEC > LOD (level of detection) being 0.01 mg/kg dw (Haarstad & Borch 2004)
River Sediment from contaminated site:
MEC > LOD in the order of 10 mg/kg dw (Swindlehurst et al 1995)
Sewage sludge:
MEC > LOD in the order of 2 mg/kg dw (Arnér et al 2004).
Water:
River delta marine water:
MEC 0.18 to 2.2 ng/L (Bester et al 2001)
River water:
MEC > 30 ng/L Somes River (Moldovan 2006)
MEC river water > 10 ng/L (Müller et al 1997)
Ground water:
MEC > 100 ng/L (Arnér et al 2004)
Leachate :
MEC > 100 ng/L (Arnér et al 2004)
Sewage water:
MEC = 4000 ng/L in untreated fraction (Arnér et al 2004), no value reported from treated water fraction
Lakewater:
MEC > LOD (Guzzella & Sora 1998)
Level in biota
Human:
Liver samples 0.1 to 1.72 ng/g fw (Ellerichmann et al 1998, IUCLID 5 section 7.10.5), which corresponds approximately to 1.3 to 39 ng/g lw
Fish:
Arctic char from freshwater concentrations ≤ 1.8 ng/g lw (Norström et al 2004)
Perch concentrations from 15 to 37 ng/g lw (Norström et al 2004) and from 38 to 100 ng/g lw (Olsson et al 1999, Olsson & Bergmann 1995) and in the muscle 32 to 190 ng/g lw (Valters et al 1999)
Herring concentrations from 29 to 31 ng/g lw (Norström et al 2004)
Salmon concentrations from 7.8 to 33 ng/g lw (Norström et al 2004)
Marine Bird egg:
White-tailed sea eagle eggs concentration 2.4 to 610 ng/g lw (Helander et al 2002) and 500 ng/g lw (Olsson & Bergmann 1995)
Guillemont egg concentrations 760 to 2600 ng/g lw (Jörundsdóttir et al 2006)
Herring Gull egg concentration not quantified (Letcher et al 1995)
Marine Bird tissues:
Baltic guillemot muscle concentrations 1600 and 1900 ng/g lw (Norström et al 2004)
Marine mammals:
Grey seal blubber tissue concentrations 41 to 210 ng/g lw (Larsson et al 2004)
Grey seal liver tissue concentrations 55 to 700 ng/g lw (Larsson et al 2004)
Grey seal lung tissue concentrations 21 to 98 ng/g lw (Larsson et al 2004)
Grey seal concentrations 49 to 480 ng/g lw (Norström et al 2004)
Remote areas
5.24 to 143 ng/g lw plasma has been reported in biota (gull blood plasma) from the Norwegian Arctic, a remote area, proving its potential for long range transport (Verreault 2005). Further arctic MEC exist (Brown et al 2008)
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