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EC number: 235-115-7 | CAS number: 12069-89-5
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
Description of key information
In a weight-of-evidence approach results are presented on the behaviour of Mo in natural samples (water, sediment, soil, suspended matter). In the reported environmental studies, analytical methods were used which are expected to provide relevant and reliable concentration levels of Mo in water and suspended matter/sediment/soil, respectively.
Key value for chemical safety assessment
Additional information
No data is available for dimolybdenum carbide (target substance). In a weight-of-evidence approach results are presented on the behaviour of Mo in natural samples (water, sediment, soil, suspended matter) at environmentally relevant temperatures. In the reported environmental studies, analytical methods were used which are expected to provide relevant and reliable concentration levels of Mo in water and suspended matter/sediment/soil, respectively. Kd values for the sediment-water system (log Kp, sediment-water) are in the range between 2.65 and 4.26, with typical EU country-specific values of 3.25 (Salminen et al., 2005). This range is consistent with the findings of the other presented studies, also reporting levels from further regions in the world. Values for the partitioning between suspended matter and water range from log Kp (suspended matter-water) = 2.19 (Popp and Laquer, 1980) to 3.9 (Neal et al., 2000), with a grand mean of 3.25, while the log Kp values for soil or soil-influenced systems range from 1.56 (Fox and Donner, 2003) to 2.6 (Buchter et al., 1989). The latter data were part of the data set that was used by Bockting et al. (1992) for deriving a typical log Kd (soil) of 2.94 for molybdenum, which was later accepted by RIVM as a relevant Kd soil for molybdenum (Crommentuijn et al., 1997).)
Other adsorption coefficient indicated as dimensionless:
- log Kp (suspended matter-water) ,3.25
- log Kp (sediment-water) ,3.25
- log Kp (soil-water) ,2.94
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