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EC number: 246-140-8 | CAS number: 24304-00-5
- 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

Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Series on Testing and Assessment No. 29 (23-Jul-2001): Guidance document on transformation/dissolution of metals and metal compounds in aqueous media
- GLP compliance:
- not specified
- Type of method:
- other: Transformation/Dissolution test
- Water solubility:
- ca. 1 087.1 µg/L
- Temp.:
- 21.5 °C
- pH:
- ca. 8
- Remarks on result:
- other: T/D test (loading 100 mg/L) at pH 8: After 7 days the mean concentrations were: 1087.1 ± 69.6 μg Al/L and 2048.0 ± 244.3 μg NH3/L
- Water solubility:
- ca. 366 µg/L
- Temp.:
- 21.5 °C
- pH:
- ca. 8
- Remarks on result:
- other: T/D test (loading 10 mg/L) at pH 8: After 7 days the mean concentrations were: 366.0 ± 11.4 μg Al/L and 664.0 ± 91.5 μg NH3/L
- Water solubility:
- ca. 202.9 µg/L
- Temp.:
- 21.5 °C
- pH:
- ca. 8
- Remarks on result:
- other: T/D test (loading 1 mg/L) at pH 8: After 28 days the mean concentrations were: 202.9 ± 14.8 μg Al/L and 146.2 ± 13.2 μg NH3/L; an equilibrium had been reached after 336 h (14d); the first order rate constant was calculated to k=0.0100 Al / h
- Details on results:
- The screening test showed aluminium releases to be slightly higher at pH 8 than at pH 6 after 24 hours. Due to the higher solubility at higher pH, pH 8 was selected to perform the full T/D test. After 7 or 28 days, as appropriate, aluminium concentrations were measured to be 202.9 ± 14.8 µg Al/L, 366.0 ± 11.4 μg Al/L and 1087.1 ± 69.6 μg Al/L for the 1, 10 and 100 mg/L sample loadings, respectively.
Equilibrium had been reached in the 1 mg/L sample loading after 336 h (14d). Hence, the first order rate constant was calculated to k = 0.0100 Al/h. - Conclusions:
- Based on the results, aluminum nitride is considered to be slightly soluble in water.
- Executive summary:
A transformation/dissolution (T/D) test in accordance with OECD Series on Testing and Assessment No. 29 was carried out to study the potential of aluminum nitride to release metal ions into the environment. A 24-hour screening test to determine the pH of maximum aluminium release was performed at pH 6 and 8 and a loading rate of 100 mg/L. The pH screening test showed aluminium releases of 981.7 ± 12.9 µg Al/L at pH 8, while the mean release of Al at pH 6 was 76.4 ± 1.1 μg Al/L. Therefore, the full T/D test was conducted at pH 8. The acute endpoint (7 days), was determined at sample loadings of 1, 10 and 100 mg/L; the chronic endpoint was determined from the extension of the 1 mg/L loading test to 28 days. The results of the study documented aluminum release measurements of 202.9 ± 14.8 µg Al/L, 366.0 ± 11.4 μg Al/L and 1087.1 ± 69.6 μg Al/L for 1, 10 and 100 mg/L sample loading respectively. Therefore, aluminum nitride is considered to be slightly soluble in water.
Reference
Table 1:Screening test: Measured dissolved Al concentrations for the loading of 100 mg/L (target pH 8: 1, 2, 3; target pH 6: 4, 5, 6 – triplicate vessels per pH, duplicate samples per vessel) |
|||||
sample |
target pH |
mean per vessel |
SD per vessel |
mean all |
SD all |
1 24h |
8 |
982.5 |
4.0 |
981.7 |
12.9 |
2 24h |
8 |
993.6 |
10.3 |
||
3 24h |
8 |
969.1 |
10.2 |
||
|
|
|
|
|
|
4 24h |
6 |
75.5 |
0.7 |
76.4 |
1.1 |
5 24h |
6 |
76.2 |
1.3 |
||
6 24h |
6 |
77.5 |
0.7 |
Table 2: Screening test: Measured dissolved NH3concentrations for the loading of 100 mg/L (target pH 8: 1, 2, 3; target pH 6: 4, 5, 6 – triplicate vessels per pH, duplicate samples per vessel) |
|||||
sample |
target pH |
mean per vessel |
SD per vessel |
mean all |
SD all |
1 24h |
8 |
753.0 |
58.9 |
726.9 |
73.5 |
2 24h |
8 |
648.0 |
56.6 |
||
3 24h |
8 |
779.7 |
30.6 |
||
|
|
|
|
|
|
4 24h |
6 |
346.3 |
16.5 |
349.7 |
10.9 |
5 24h |
6 |
346.3 |
7.1 |
||
6 24h |
6 |
356.3 |
11.8 |
Description of key information
In a transformation/dissolution test aluminium nitride proved to be slightly soluble, releasing maximum aluminium concentrations of 1087.1 µg/L and total ammonia (NH3) of maximally 2048 µg/L (at 100 mg/L nominal loading after 7 days).
Key value for chemical safety assessment
- Water solubility:
- 1 087.1 µg/L
- at the temperature of:
- 21.5 °C
Additional information
A transformation/dissolution (T/D) test in accordance with OECD Series on Testing and Assessment No. 29 was carried out to study the potential of aluminium nitride to release metal ions into the environment. A 24-hour screening test to determine the pH of maximum aluminium release was performed at pH 6 and 8 and a loading rate of 100 mg/L. The pH screening test showed aluminium releases of 981.7 ± 12.9 µg Al/L at pH 8, while the mean release of Al at pH 6 was 76.4 ± 1.1 μg Al/L. Therefore, the full T/D test was conducted at pH 8. The acute endpoint (7 days), was determined at sample loadings of 1, 10 and 100 mg/L; the chronic endpoint was determined from the extension of the 1 mg/L loading test to 28 days. The results of the study documented aluminium release measurements of 202.9 ± 14.8 µg Al/L, 366.0 ± 11.4 μg Al/L and 1087.1 ± 69.6 μg Al/L for 1, 10 and 100 mg/L sample loading respectively. Therefore, aluminium nitride is considered to be slightly soluble in water.
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