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Diss Factsheets
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EC number: 204-112-2 | CAS number: 115-86-6
- 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
Monitoring studies have been carried out on the air quality of domestic houses and offices. For domestic houses TPP was detected in two of the six houses monitored at a concentration of 0.01 µg/m3. In another study of public buildings both indoor and outdoor air contained <0.01 µg/m3, in indoor particulate matter 220 mg/kg TPP were found in one sample but all other samples had concentrations of <= 3 mg/kg. Monitoring was also carried out in offices in which new computer equipment was installed. Before installation, and in offices not containing the equipment, air concentrations were 0.7 ng/m3, this increased to 84 ng/m3one day after installation and decreased to 39 ng/m3after eight days. . In a smaller office with brand-new computer equipment, the TPP level was 94 ng/m3one day after computer installation. This had decreased to 10 ng/m3within 150days.
Monitoring studies have also been carried out on rivers. The level of TPP in the river Ruhr increased from values below the limit of detection at its source to values of 200 ng/L in the Dortmund region. In two tributaries values of 400 ng/L were found. Even higher values were found in a creek dominated by asewage works (2000 ng/L) and in the river Emscher (3400 ng/L). However, bankfiltered ground water contained <1 ng/L - the detection limit.
Additional information
Monitoring of sewage treatment plants in the US showed that there was an eight fold decrease in TPP concentration, from 16 µg/L to 2 µg/L, between the inlet and outlet of the treatment plant. In another study in Sweden concentrations of 3 µg/L of TPP were found in the sewage outlet of one of three reatment plants tested. In Germany a small creek which was dominated by the outflow of a sewage treatment plant, 2 µg/l were found. TPP concentrations reached up to 0.280 µg/l in the river Ruhr (region with heavy industry and mining) in Germany, whilst in the Delaware river in the US concentrations of up to 0.3 µg/L were found. In another study from the US TPP was found in 14.1 % of 85 samples with a median of 0.040 µg/l and a maximum value of 0.22 µg/L.
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