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EC number: 232-192-9 | CAS number: 7789-82-4
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Principles of method if other than guideline:
- Two vessels were set up in a parallel design at 20 ± 1.0 °C, each solution was sampled repeatedly over time instead of setting up multiple vessels and sampling solutions from a different vessel at each sampling date. This modification helps to minimize weighing errors as larger amounts are being handled.
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 2011-02-07
- Type of method:
- flask method
- Water solubility:
- 39.57 mg/L
- Conc. based on:
- test mat.
- Loading of aqueous phase:
- 1 000 mg/L
- Incubation duration:
- >= 1 - <= 3 d
- Temp.:
- 20.8 °C
- pH:
- >= 7.1 - <= 7.7
- Water solubility:
- 18.43 mg/L
- Conc. based on:
- element
- Remarks:
- molybdenum
- Loading of aqueous phase:
- 1 000 mg/L
- Incubation duration:
- >= 1 - <= 3 d
- Temp.:
- 20.8 °C
- pH:
- >= 7.1 - <= 7.7
- Details on results:
- Observations
During the study, undissolved test material was observed in the test vessels. To verify the reliability of the filtration step and thus that only dissolved metal concentrations would get measured, turbidity was measured in a filtered sample directly after sampling.
Temperature
The temperature was monitored using a Testo Data Logger. The mean temperature was 20.8 ± 0.3 °C.
Solution pH
Solution pH in samples containing the test item were at 7.1 - 7.7 while the pH in method blanks ranged from 6.1 to 6.3.
Turbidity
The turbidity was measured after filtration to verify that only dissolved metal concentrations would get measured. The turbidity was always <<1 NTU, indicating that there was not any undissolved material after the filtration step.
Dissolved metal concentrations
Due to low limits of quantification and a potential cross-contamination by the electrodes for pH measurements, calcium levels in method blanks were above the limits of quantification (LOQ = 0.418 - 0.572 µg Ca/L) but well below concentrations in samples containing the test item (<< 1 %). Molybdenum concentrations in method blanks were below the respective limits of detection (LOD = 1.133– 1.379 µg Mo/L). Test samples containing the test item were diluted (dilution factor 100) so that the respective metal concentrations would be in the calibrated range of the ICP-OES instrument. - Conclusions:
- Interpretation of results: slightly soluble (0.1-100 mg/L)
The water solubility of calcium molybdate is 39.57 mg/L at 20.8 °C (pH 7.1 - 7.7 in the saturated solution)
Reference
Method validation summary
validation parameter |
results |
comment |
selectivity |
similar data with at least two different molybdenum and calcium wavelengths for ICP-OES method |
matrix effects were not observed |
linearity |
applied calibration functions were linear |
correlation coefficient at least 0.999806
|
limits of detection (LOD)
|
1.133 – 1.379 µg Mo/L 0.139 – 0.191 µg Ca/L |
|
limits of quantification (LOQ)
|
3.399 –4.137 µg Mo/L 0.418 - 0.572 µg Ca/L |
|
concentrations in method blanks |
Ca: above LOQ but far below concentrations in samples containing the test item (<< 1 %) Mo: < LODs (<3.399 –4.137 µg Mo/L) |
- |
accuracy and precision, repeatability |
mean recovery for TMDA-53.3 reference material: Mo: (dilution factor 10, 25.5 µg Mo/L): 98.3 ± 5.3 % (n = 5) |
for concentration range of diluted samples and for fortification and method blanks
|
accuracy and precision, repeatability |
mean recovery for Quality Control Standard Mo: (50 µg Mo/L): 97.2 ± 1.6 % (n = 5) |
for concentration range of diluted samples and for fortification and method blanks |
accuracy and precision |
mean recovery for Quality Control Standard Ca: (50 µg Ca/L): 108 ± <1 % (n = 2) |
for concentration range of diluted samples and for fortification and method blanks |
accuracy and precision, repeatability |
mean recovery for recalibration Mo: (10 µg Mo/L): 101.3 ± 10.1 % (n = 4) Ca: (10 µg Mo/L): 104.2 ± 6.2 % (n = 5) |
for concentration range of diluted samples and for fortification and method blanks |
trueness |
recovery from fortification of samples: Mo: 98.1 - 102.4 % (n = 6) Ca: 98.2 - 102.9 % (n = 6) |
|
Results
The mean dissolved molybdenum concentrations of solutions sampled on day 1, day 2 and day 3 were calculated. Mean dissolved Mo concentrations day 1 – day 3:
Vessel 1: 18.16 ± 0.42 mg/L
Vessel 2: 18.70 ± 0.45 mg/L
Mean for both vessels: 18.43 ± 0.5 mg/L
The amount of dissolved calcium molybdate was calculated based on the molybdenum content of the test substance as follows:
= mean of measured Mo concentration * 100 % / 46.58 % [Mo content of test item, as per certificate of analysis provided by the sample producer]
mean calculated water solubility of calcium molybdate (based on dissolved Mo) , day 1 – day 3:
Vessel 1: 38.99 ± 0.90 mg/L
Vessel 2: 40.16 ± 0.96 mg/L
Mean for both vessels: 39.57 ± 1.08 mg/L
Dissolved measured Ca concentrations were lower than expected and correspondingly the calculated solubility of the test item was approx. 27% lower when based on analysed dissolved Ca than when based on analysed dissolved Mo (waters solubility = 39.57 mg/L based on Mo, compared 28.77 mg/L based on Ca). It is assumed that this is due to the formation of poorly soluble, possibly colloidal calcium species (such as calcium carbonate), that have not passed the filter before analysis. Using the analysed dissolved Mo to calculate the solubility of the test item calcium molybdate provides the higher final solubility figure. Since this is also the more conservative figure in a regulatory context, it is taken forward as the final result.
Final results
Under the conditions of this test flask method; loadings of 1000.2 mg/L in vessel 1 and 2, respectively), a solubility equilibrium was reached during the first three days of testing. The mean measured amount of dissolved Mo on day 1, day 2 and day 3 at 20.0 ± 1.0°C is 18.43 ± 0.50 mg/L (determined as dissolved Mo, separated by filtration from undissolved test item). This corresponds to a water solubility of calcium molybdate of 39.57 ± 1.08 mg/L, calculated based on a molybdenum content of 46.58 %. Solution pH in samples containing the test item were at 7.1 - 7.7 while the pH in method blanks ranged from 6.1 to 6.3.
Description of key information
The water solubility of calcium molybdate has been determined experimentally (OECD TG 105 study, GLP) to be 39.6 mg/L at 20 °C. The pH of the saturated solution was 7.1 - 7.7.
In addition to the standard OECD TG 105 water solubility study, the substance has also been tested in a bioelution study (in vitro bioaccessibility) in artificial gastric juice. This test and the results are described in the stand-alone document „MoCon read-across concept (human health)“, which is attached to the technical dossier in IUCLID section 13.
Key value for chemical safety assessment
- Water solubility:
- 39.6 mg/L
- at the temperature of:
- 20 °C
Additional information
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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