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EC number: 234-722-4 | CAS number: 12027-67-7
- 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
Toxicity to terrestrial plants
Administrative data
Link to relevant study record(s)
Description of key information
A total of 10 topsoils with contrasting properties that may affect the toxicity of Mo in soil were collected and on each of these soils a series of 5 plant assays (root elongation for barley and shoot yield for oilseed rape, red clover, ryegrass and tomato) were performed after spiking with sodium molybdate. The plant toxicity assays resulted in 45 individual high quality EC10 values selected for PNEC derivation. The EC10 values ranged from 4 to 3476 mg added Mo/kg dry weight soil.
Additionally, 3 soils were aged outdoors after spiking with sodium molybdate. After 6 and 11 months, subsamples were collected and the 4 ecotoxicity tests (same as above without barley root elongation assay) were conducted on these soils. In general, this showed that long-term equilibration of Mo in soils decreases its toxicity to plants. The results of the toxicity in aged soils are used to determine a Leaching/Ageing factor to correct for the effect of spiking on the toxicity of Mo in soil organisms.
Key value for chemical safety assessment
Additional information
Available reliable data on the soil type-specific toxicity of molybdenum to terrestrial plants were available for Brassica napus, Trifolium pratense, Lolium perenne, Lycopersicon esculentum, Hordeum vulgare, Zea mays, Daucus carota and Pisum sativum. A total of 45 individual high quality EC10 values (for 5 different plant species) were selected for the PNEC derivation, ranging from 4 mg added Mo/kg dw (for oilseed and red clover) to 3476 mg added Mo/kg dw (for ryegrass) All data are based on added measured Mo concentrations in soil. For 5 dose-response-curves, no reliable EC10 or NOEC could be derived because a significant effect was already seen at the lowest dose tested. For the aged soils the comparison of Mo in freshly spiked and 11 -month aged soils show that long-term equilibration of Mo in soil generally decreases its toxicity in plants. Only in one case (out of 12 cases) there was an effect at a lower dose in the aged soil. The results of the toxicity in aged soils were used to determine a leaching/ageing factor to correct for the effect of spiking on the toxicity of Mo in soil organisms.
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