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EC number: 700-042-6 | CAS number: 177997-13-6
- 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
![](https://www.echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_ecotoxicological-information.png)
Additional ecotoxological information
Administrative data
- Endpoint:
- additional ecotoxicological information
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Not specified.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Experimental design that follows the recommendations of the OECD guidance document on transformation/dissolution (T/D) (OECD 2001)(1) and the standard operating procedures (SOP) proposed by CANMET and LISEC(2) for the Dissolution Transformation protocol to the ad hoc OECD Validation Management Group (VMG). (1)OECD Guideline for testing of chemicals - draft proposal - February 2001. Transformation dissolution of metals and metal compounds in aqueous media. (2)The Standard Operating Procedure for the Transformation/Dissolution of Metals and Sparingly Soluble Metal Compounds, Version February 2004.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Experimental design that follows the recommendations of the OECD guidance document on transformation/dissolution (T/D) (OECD 2001)(1) and the standard operating procedures (SOP) proposed by CANMET and LISEC(2) for the Dissolution Transformation protocol
- Deviations:
- no
- GLP compliance:
- not specified
- Type of study / information:
- The report aims to describe the transformation/dissolution behavior of Cellcore QX.
Test material
- Reference substance name:
- aluminium(3+) nickel(2+) λ²-cobalt(2+) lithium(1+) tetraoxidandiide
- EC Number:
- 700-042-6
- Cas Number:
- 177997-13-6
- Molecular formula:
- LiNiCoAlO2 where stoichiometry of Ni+Co+Al equals 1 and ranges are Li = 0.9 – 1.3, Co = 0.01 – 0.2, Ni = 0.75 – 0.99 and Al = 0.01 – 0.2
- IUPAC Name:
- aluminium(3+) nickel(2+) λ²-cobalt(2+) lithium(1+) tetraoxidandiide
- Details on test material:
- - Name of test material (as cited in study report): Cellcore QX
- Substance type: Inorganic
- Physical state: Black powder
-molecular formula LiNiCoAlO2. The stoechiometry of Ni+Co+Al equals 1 but the nickel, cobalt and aluminium content can vary. The sample provided for this test had a composition of LiNi0.8Co0.15Al0.05O2.
Constituent 1
Results and discussion
Any other information on results incl. tables
Samples of a commercially available complex called oxide Cellcore QX were first tested in a screening test at pH 6, 7 and 8 at 100 mg/l loading. The results indicated that the maximum release of Aluminium and Lithium were almost independent of the pH. Cobalt and Nickel showed the maximum release at pH 6. Since Cobalt and Nickel are more relevant to environmental toxicity than Lithium and Aluminium a pH 6 was selected to perform the full 7 days tests (acute toxicity) at the 3 recommended loadings (1, 10, 100 mg/l). Also the chronic 28 days tests at 1mg/l loading were performed.
The results are summarized in the tables below and can be used to compare with existing ecotoxicity reference values to establish the aquatic hazard classification of the tested substance.
Table 1.- Screening test: summary of dissolution transformation test for 24 hours at pHs 6, 7 and 8, 200 RPM and 100 mg/L loading.
pH 6.0 |
||||||||||||
Time, h |
Li, μg/L |
SD |
Al, μg/L |
SD |
Co, μg/L |
SD |
Ni, μg/L |
SD |
||||
0 h |
657.6 |
3.3 |
94.2 |
17 |
0.47 |
0.29 |
13.1 |
0.1 |
||||
24 h |
801.4 |
37.8 |
54.2 |
12 |
7.83 |
0.17 |
91.0 |
3.5 |
||||
|
|
pH 7.0 |
|
|
||||||||
Time, h |
Li, μg/L |
SD |
Al, μg/L |
SD |
Co, μg/L |
SD |
Ni, μg/L |
SD |
||||
0 h |
661.7 |
37.6 |
181 |
2 |
0.40 |
0.05 |
10.8 |
0.2 |
||||
24 h |
909.0 |
16.2 |
81 |
1 |
3.16 |
0.03 |
43.6 |
0.8 |
||||
|
|
pH 8.0 |
|
|
||||||||
Time, h |
Li, μg/L |
SD |
Al, μg/L |
SD |
Co, μg/L |
SD |
Ni, μg/L |
SD |
||||
0 h |
656.4 |
3.2 |
171 |
3 |
0.34 |
0.07 |
14.7 |
0.7 |
||||
24 h |
937.9 |
9.6 |
136 |
1 |
2.96 |
0.05 |
61.3 |
0.2 |
Table 2.- 7 and 28 days tests: summary of dissolution transformation test for 7 days at pH 6, 100 RPM at 1, 10 and 100 mg/L loading and 28 days 1mg/L loading.
1 mg/L, pH 6 |
||||||||||
Time, h |
Li, μg/L |
SD |
Al, μg/L |
SD |
Co, μg/L |
SD |
Ni, μg/L |
SD |
||
0 h |
5.9 |
1.0 |
4 |
- |
0.04 |
0.03 |
0.4 |
0.1 |
||
168 h |
12.6 |
0.4 |
3 |
- |
1.35 |
0.24 |
8.0 |
1.2 |
||
672 h |
16.9 |
1.0 |
BDL |
- |
1.72 |
0.28 |
10.7 |
1.7 |
||
10 mg/L, pH 6 |
||||||||||
Time, h |
Li, μg/L |
SD |
Al, μg/L |
SD |
Co, μg/L |
SD |
Ni, μg/L |
SD |
||
0 h |
59.6 |
4.7 |
2 |
- |
0.15 |
0.02 |
3.1 |
0.5 |
||
168 h |
92.3 |
1.8 |
2 |
0.4 |
3.46 |
0.25 |
28.4 |
1.7 |
||
100 mg/L, pH 6 |
||||||||||
Time, h |
Li, μg/L |
SD |
Al, μg/L |
SD |
Co, μg/L |
SD |
Ni, μg/L |
SD |
||
0 h |
692.8 |
7.0 |
36 |
5 |
|
0.74 |
0.06 |
21.1 |
0.6 |
|
168 h |
997.4 |
16.8 |
17 |
4 |
13.59 |
1.29 |
148.0 |
9.1 |
The elemental reference values used for the comparison were produced from literature values (please see attached background material for the relevant reports used to determine the elemental toxicity reference values).
Based on the transformation/dissolution study Cobalt and Nickel are considered more relevant to environmental toxicity than Lithium and Aluminium.
In comparison to the study values observed at the pH of maximum metal release (pH6) in both 7 day test and 28 days test, with the ecotoxicity reference values it is proposed that the substance is classified as Aquatic Chronic category 3. Please see attached backgroud material for the document comparing the results and the reasoning for the proposed environmental classification based upon CLP guidance.
Applicant's summary and conclusion
- Conclusions:
- The substance is classified as Aquatic Chronic category 3. based upon a comparison between the results of a transformation/dissolution test (to measure the amount of metal released from the substance) and ecotoxicity reference values for the elements.
- Executive summary:
The transformation / dissolution of Cellcore QX was tested in accordance to the draft OECD Transformation/Dissolution protocol. The experimental design includes refinements, agreed by the ad hoc OECD Validation Management Group (VMG), as described in the Standard Operating Procedures prepared by CANMET and LISEC. Samples of a commercially available complex called oxide Cellcore QX were first tested in a screening test at pH 6, 7 and 8 at 100 mg/l loading. The results indicated that the maximum release of Aluminium and Lithium were almost independent of the pH. Cobalt and Nickel showed the maximum release at pH 6. Since Cobalt and Nickel are more relevant to environmental toxicity than Lithium and Aluminium a pH 6 was selected to perform the full 7 days tests (acute toxicity) at the 3 recommended loadings (1, 10, 100 mg/l). Also the chronic 28 days tests at 1mg/l loading were performed.
The results are summarized in the tables below and can be used to compare with existing ecotoxicity reference values to establish the aquatic hazard classification of the tested substance.
Table 1.- Screening test: summary of dissolution transformation test for 24 hours at pHs 6, 7 and 8, 200 RPM and 100 mg/L loading.
pH 6.0
Time, h
Li, μg/L
SD
Al, μg/L
SD
Co, μg/L
SD
Ni, μg/L
SD
0 h
657.6
3.3
94.2
17
0.47
0.29
13.1
0.1
24 h
801.4
37.8
54.2
12
7.83
0.17
91.0
3.5
pH 7.0
Time, h
Li, μg/L
SD
Al, μg/L
SD
Co, μg/L
SD
Ni, μg/L
SD
0 h
661.7
37.6
181
2
0.40
0.05
10.8
0.2
24 h
909.0
16.2
81
1
3.16
0.03
43.6
0.8
pH 8.0
Time, h
Li, μg/L
SD
Al, μg/L
SD
Co, μg/L
SD
Ni, μg/L
SD
0 h
656.4
3.2
171
3
0.34
0.07
14.7
0.7
24 h
937.9
9.6
136
1
2.96
0.05
61.3
0.2
Table 2.- 7 and 28 days tests: summary of dissolution transformation test for 7 days at pH 6, 100 RPM at 1, 10 and 100 mg/L loading and 28 days 1mg/L loading.
1 mg/L,pH 6
Time, h
Li, μg/L
SD
Al, μg/L
SD
Co, μg/L
SD
Ni, μg/L
SD
0 h
5.9
1.0
4
-
0.04
0.03
0.4
0.1
168 h
12.6
0.4
3
-
1.35
0.24
8.0
1.2
672 h
16.9
1.0
BDL
-
1.72
0.28
10.7
1.7
10 mg/L,pH 6
Time, h
Li, μg/L
SD
Al, μg/L
SD
Co, μg/L
SD
Ni, μg/L
SD
0 h
59.6
4.7
2
-
0.15
0.02
3.1
0.5
168 h
92.3
1.8
2
0.4
3.46
0.25
28.4
1.7
100 mg/L,pH 6
Time, h
Li, μg/L
SD
Al, μg/L
SD
Co, μg/L
SD
Ni, μg/L
SD
0 h
692.8
7.0
36
5
0.74
0.06
21.1
0.6
168 h
997.4
16.8
17
4
13.59
1.29
148.0
9.1
Cellcore QX has been assessed for environmental effects using the T/D protocol as appropriate for poorly soluble metal compounds. The full test was conducted at pH6 due to the max. solubility of Ni and Co. Results were compared to the relevant ERV and the additivity rule was applied. Based on the available data the registrant concludes that Cellcore QX should be classified as Aquatic Chronic category 3 under Regulation EC nr. 1272/2008 (CLP) and R52/53 under Directive 67/548/EC (DSD).
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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