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EC number: 209-062-5 | CAS number: 554-13-2
- 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

Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1996-08-14 to 1997-02-02-04
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 1984
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OTS 797.1300 (Aquatic Invertebrate Acute Toxicity Test, Freshwater Daphnids)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Samples were analyzed for lithium in triplicate using a FLM-AAS method developed and validated by the FMC Corporation. Measured concentrations of lithium carbonate were calculated by multiplying measured lithium concentrations by 5.3240.
- Vehicle:
- no
- Details on test solutions:
- A primary stock solution (5000 mg wm/L) was prepared for the definitive test by adding 1.2500 g of neat test substance to 250 mL volumetric flask, bringing it to volume with deionized water and sonicating for approximately 50 minutes to ensure homogeneity. Test solutions were prepared by adding appropriate volumes of the primary stock to the appropriate volume of dilution water (total volume 1 liter). A dilution water control was maintained concurrently with the test solutions.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Water fleas will be neonates (i.e. <24 hours old) obtained by isolating gravid females from the culture water in food-free dilution water < 24 hours prior to beginning the test.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- No
- Hardness:
- c(CaCO3) = 56 mg wm/L
- Test temperature:
- 19.0 °C to 20.3 °C
- pH:
- pH 8.5 to 10.2
- Dissolved oxygen:
- 7.2 to 8.9 mg/L (79 to 98 % of saturation)
- Nominal and measured concentrations:
- Nominal concentrations: 5.0, 10, 20, 40, and 80 mg/L
Measured concentrations: 0.0, 4.76, 9.84, 20.0, 43.7 and 82.8 mg/L - Reference substance (positive control):
- no
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 33.2 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Remarks:
- Li2CO3
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CL: 20.0 - 42.7 mg wm/L
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 20 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Remarks:
- Li2CO3
- Basis for effect:
- mobility
- Details on results:
- The 48-hour EC50 was 33.2 mg/L (based on mean measured concentrations) with 95 % confidence limits of 20.0 and 43.7 mg/L. The no-observed-effect-concentration (NOEC) was 20.0 mg/L, based on the lack of mortality and sublethal effects at this and all lower test concentrations.
- Reported statistics and error estimates:
- The EC50 values were estimated by a computer program (Wheat, 1989) using the following statistical methods: moving average angle, probit, logit, and non-linear interpolation. Confidence limits for EC50 values determined by non-linear interpolation were calculated by binomial probability. The method selected for reporting the test results was determined by the characteristics of the data, i.e. the presence or absence of 0 % and 100 % mortality and the number of concentrations in which mortalities between 0 and 100 % occurred.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The 48-hour EC50 in Daphnia magna was 33.2 mg lithium carbonate/L (based on mean measured concentrations) with 95 % confidence limits of 20.0 and 43.7 mg lithium carbonate/L.
The NOEC was 20.0 mg lithiumcarbonate/L, based on the lack of mortality and sublethal effects at this and all lower test concentrations. - Executive summary:
A static freshwater toxicity test was conducted to determine the acute toxicity of lithium carbonate to the water flea, Daphnia magna according to OECD Guideline 202. Mean measured concentrations of lithium carbonate ranged from 4.76 to 82.8 mg/L and from 95 to 109 % of nominal. All test solutions appeared clear and colourless and concentrations remained stable throughout the test. Mortality of the water flea exposed for 48 hours to lithium carbonate ranged from 0 % at test concentrations lower than 20.0 mg/L to 100 % at 82.8 mg/L. Control mortality was 0 %. The 48-hour EC50 was 33.2 mg lithium carbonate/L with 95 % confidence limits of 20.0 and 43.7 mg/L. The NOEC was 20.0 mg lithium carbonate/L, based on a lack of significant mortality and sublethal effects observed at this and all lower test concentrations. Based on these data, the calculated EC50 for lithium ion was 6.24 mg/L and the NOEC was 3.76 mg/L.
Reference
Mortality of the water flea, Daphnia magna, during a 48 -hour exposure to lithium carbonate under static conditions:
Mean Measured Concentration |
Cumulative Number Dead (Percent Mortality) |
|||
24 Hour |
48 Hour |
|||
Control |
0 |
(0) |
0 |
(0) |
4.76 |
0 |
(0) |
0 |
(0) |
9.84 |
0 |
(0) |
0 |
(0) |
20.0 |
0 |
(0) |
0 |
(0) |
43.7 |
9 |
(45) |
17 |
(85) |
82.8 |
15 |
(75) |
20 |
(100) |
Calculated EC50 values, based upon measured concentrations, for the water flea, Daphnia magna, exposed to lithium carbonate under static conditions:
Exposure Period (Hour) |
EC50Valuea |
LCLb |
UCLc |
Slope |
Method Used |
24 |
53.3 |
43.1 |
67.8 |
4.43 |
Probit |
48 |
33.2 |
20.0 |
43.7 |
-.-d |
Binomial |
a EC50 values and confidence limits expressed in mg wm/L.
b Lower 95 percent confidence limit.
c Upper 95 percent confidence limit.
d The slope cannot be calculated using this method.
Description of key information
The 48-hour EC50 in Daphnia magna was 33.2 mg lithium carbonate/L (based on mean measured concentrations) with 95 % confidence limits of 20.0 and 43.7 mg lithium carbonate/L. The NOEC was 20.0 mg lithium carbonate/L, based on the lack of mortality and sublethal effects at this and all lower test concentrations.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 33.2 mg/L
Additional information
A static freshwater toxicity test was conducted to determine the acute toxicity of lithium carbonate to the water flea, Daphnia magna according to OECD Guideline 202. Mean measured concentrations of lithium carbonate ranged from 4.76 to 82.8 mg/L and from 95 to 109 % of nominal. All test solutions appeared clear and colourless and concentrations remained stable throughout the test. Mortality of the water flea exposed for 48 hours to lithium carbonate ranged from 0 % at test concentrations lower than 20.0 mg/L to 100 % at 82.8 mg/L. Control mortality was 0 %. The 48-hour EC50 was 33.2 mg lithium carbonate/L with 95 % confidence limits of 20.0 and 43.7 mg/L. The NOEC was 20.0 mg lithium carbonate/L, based on a lack of significant mortality and sublethal effects observed at this and all lower test concentrations. Based on these data, the calculated EC50 for lithium ion was 6.24 mg/L and the NOEC was 3.76 mg/L.
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