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EC number: 269-682-7 | CAS number: 68309-95-5
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 4 January 2012
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study not conducted to GLP but conducted in accordance with generally accepted scientific principles based on a standard OECD method.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
- Report date:
- 2012
Materials and methods
- Objective of study:
- other: determination of the behaviour of the substance at low pH in order to provide comparison with the similar substance KZC.
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: OECD 111
- Deviations:
- yes
- Remarks:
- The study was conducted at pH 2 and pH 4. Due to the very fast hydrolysis of the substance under acidic conditions and the slow release of CO2 from the solution, it was decided not to perform kinetic measurements.
- Principles of method if other than guideline:
- The purpose of this study was to determine the hydrolysis under evolution of carbon dioxide of Ammonium Zirconium Carbonate (AZC) at pH 2.00 and pH 4.00. Gas absorption on sodium hydroxide (on a support material) is used to determine the cleavable amount of carbon dioxide from AZC in acidic solution at two different pH values.
- GLP compliance:
- no
Test material
- Reference substance name:
- Ammonium Zirconium Carbonate
- IUPAC Name:
- Ammonium Zirconium Carbonate
- Test material form:
- other: liquid
Constituent 1
Results and discussion
Any other information on results incl. tables
RESULTS, pH 2.00
Sample |
Acid |
Temperature |
Reac- |
pH at the end |
CO32-con- |
CO2 |
CO32-calculated |
CO32- |
[g] |
[mL] |
[°C] |
[min] |
|
[%] |
[g] |
[g] |
[%] |
0.6618 |
100.0 |
25 |
40 |
2.34 |
17 |
0.0805 |
0.1098 |
16.59 |
0.6620 |
100.0 |
25 |
40 |
2.34 |
17 |
0.0799 |
0.1090 |
16.46 |
0.6605 |
150.0 |
25 |
40 |
2.32 |
17 |
0.0843 |
0.1150 |
17.40 |
0.6857 |
150.0 |
25 |
40 |
2.17 |
17 |
0.0883 |
0.1204 |
17.56 |
0.6710 |
150.0 |
25 |
40 |
2.17 |
17 |
0.0834 |
0.1137 |
16.95 |
The amount of CO2 found after hydrolysis is equal to a carbonate content of 17.0 ± 0.4 % in AZC tested substance.
RESULTS, pH 4.00
Sample |
Acid |
Temperature |
Reac- |
pH at the end |
CO32-con- |
CO2 |
CO32-calculated |
CO32- |
[g] |
[mL] |
[°C] |
[min] |
|
[%] |
[g] |
[g] |
[%] |
0.6741 |
100.0 |
65 - 70 |
100 |
4.10 |
17 |
0.0823 |
0.1122 |
16.65 |
0.6700 |
100.0 |
65 - 70 |
100 |
4.10 |
17 |
0.0858 |
0.1170 |
17.46 |
0.6697 |
100.0 |
65 - 70 |
100 |
4.10 |
17 |
0.0801 |
0.1092 |
16.31 |
The amount of CO2 found after hydrolysis is equal to a carbonate content of 16.80 ± 0.5 % in AZC tested substance.
IDENTIFICATION OF HYDROLYSIS PRODUCTS
One hydrolysis product of AZC is carbon dioxide. The remaining zirconium compounds are not identified.
Applicant's summary and conclusion
- Conclusions:
- The experiments at pH 2 and 4 show fast hydrolysis of AZC. This hydrolysis is observed via effervescence during addition of the acidic buffer solution. The fast hydrolysis and the fact that the CO2 release from the solution is slow did not allow kinetic information to be obtained.
The experiments showed that the CO2 released during the hydrolysis reaction corresponds to the carbonate content of AZC as given by the supplier. Based on this information, it can be concluded that AZC undergoes complete degradation under acidic conditions in a few minutes. - Executive summary:
A study was conducted to investigate the hydrolysis of the test material under acidic conditions, broadly in accordance with OECD guideline 111.
Gas absorption on sodium hydroxide (on a support material) is used to determine the cleavable amount of carbon dioxide from AZC in acidic solution at two different pH values.
The experiments at pH 2 and 4 show fast hydrolysis of AZC. This hydrolysis is observed via effervescence during addition of the acidic buffer solution. The fast hydrolysis and the fact that the CO2 release from the solution is slow did not allow kinetic information to be obtained. The experiments showed that the CO2 released during the hydrolysis reaction corresponds to the carbonate content of AZC as given by the supplier. Based on this information, it can be concluded that AZC undergoes complete degradation under acidic conditions in a few minutes.
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