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EC number: 234-454-8 | CAS number: 12004-35-2
- 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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
No data on the long term toxicity to aquatic invertebrates are available for the test substance Nickel aluminate. However, there are reliable data available for different structurally analogue test substances.
The environmental fate pathways and ecotoxicity effects assessments for Ni metal and Ni compounds is based on the observation that adverse effects to aquatic, soil- and sediment-dwelling organisms are a consequence of exposure to the bioavailable Ni-ion, released by the parent compound. The result of this assumption is that the ecotoxicology will be similar for all soluble Ni substances used in the ecotoxicity experiments. Therefore, data from soluble nickel substances are used in the derivation of ecotoxicological and environmental fate endpoints, based on the Ni-ion.
Freshwater:
From the database of chronic nickel toxicity to freshwater invertebrates, 113 individual EC10 or NOEC values for 15 different individual species were selected. Chronic data on invertebrates belonging to different taxonomic groups being cladoceran (79% of the data points), amphipods (0.9% of the data), insects (7% of the data), hydrozoans (0.9% of the data), rotifers (5% of the data) and a mollusc (7% of the data). The NOEC/L(E)C10 varied between 1.4 μg Ni/L for C. dubia (Wirtz et al., 2004) and 1193.3 μg Ni/L for Chironomus tentans (Stubblefield and Van Genderen 2007). It is noted that the invertebrate data are heavily dominated by data on cladocerans.
The following table indicates those NOEC or EC10 values of high quality that have been carried forward for the HC5-& PNEC derivation
Key Study (freshwater invertebrates) |
Selected values for the most sensitive endpoints used for derivation of the freshwater HC5 |
||
Species |
Endpoint |
Value (s) (µg/L) |
|
Delebeeck et al., 2005 |
Daphnia magna |
NOEC/EC10 |
8.8-256 |
Kunh et al., 1989 |
Daphnia magna |
NOEC |
90 |
Munzinger, 1990 |
Daphnia magna |
NOEC |
40 |
Munzinger, 1994 |
Daphnia magna |
NOEC |
80 |
Keithly et al., 1994 |
Ceriodaphnia dubia |
NOEC |
3.4-5.8 |
Wirtz et al., 2004 |
Ceriodaphnia dubia |
EC10 |
2.8-7.6 |
De Schamphelaere et al., 2006 |
Ceriodaphnia dubia |
EC10 |
7.4-44.2 |
Nebeker et al., 1984 |
Clistorina magnifica |
NOEC |
66 |
Nebeker et al., 1986 |
Juga plicifera |
NOEC |
124 |
Santiago-Fandino, 1983 |
Hydra littoralis |
NOEC |
60 |
Keithly et al., 2004 |
Hyalella azteca |
NOEC |
29 |
Deleebeeck et al., 2006 |
Ceriodaphnia quadrangular |
NOEC |
2.0-12.7 |
Peracantha truncata |
NOEC |
2.5-25.8 |
|
Daphnia longispina |
NOEC |
26.6-29.0 |
|
Alona affinis |
NOEC |
25.0 |
|
Ceriodaphnia pulchella |
NOEC |
9.9-28.2 |
|
Simocephalus vetulus |
NOEC |
9.2-28.9 |
|
Stubblefield and Van Genderen, 2007 |
Lymnaea stagnalis |
EC10 |
1.4 -19.5 |
Brachionus calyciflorus |
EC10 |
498 -1379 |
|
Chironomustentans |
EC10 |
404 -782 |
Marine:
From the database of chronic nickel toxicity to marine invertebrates, EC10 values are reported for 10 species. EC10 values range from 22.9 μg Ni/L for reproduction of the polychaete, Neanthes arenaceodenata (Parametrix, 2007f) to 431 μg Ni/L for development of the bivalve, Crassostrea gigas (Parametrix 2007g). The table below represents the NOEC or EC10 values of high quality carried forward for derivation of HC5 and aquatic marine PNEC.
Key Study (marine invertebrates) |
Selected values for the most sensitive endpoints used for derivation of the marine HC5 |
||
Species |
Endpoint |
Value (s) (ug/L) |
|
Parametrix 2007d |
Strongylocentrotus purpuratus |
EC10 |
335 |
Dendraster excentricus |
EC10 |
191 |
|
Hunt et al., 2002 |
Mysidopsis intii |
EC10 |
45.2 |
Haliotis rufescens |
EC10 |
36.4 |
|
Gentile et al., 1982 |
Mysidopsis bahia |
LOEC |
141 |
Mysidopsis bahia |
NOEC |
61 |
|
Parametrix 2007e |
Mytilius galloprovincialis |
EC10 |
269.7 (geomean) |
Parametrix 2007f |
Neanthes arenaceodentata |
EC10 |
22.5 |
Parametrix 2007g |
Crassostrea gigas |
EC10 |
431 |
Novella et al., 2003 |
Paracentrotus lividus |
EC10 |
89 |
Pagano, 2007 |
Paracentrotus lividus |
EC10 |
217 |
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