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EC number: 700-327-5 | CAS number: 1061328-86-6
- 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
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2009
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: No standardized experimental procedure, scientific principles are met.
- Principles of method if other than guideline:
- Chelate stability test. Interaction experiment of iron chelates at different pH values and with presence of Ca2+, which may compete with Fe3+ in calcareous soils.
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
No surrogate or analogue material was used. - Radiolabelling:
- not specified
- Analytical monitoring:
- no
- Details on sampling:
- No details available.
- Buffers:
- pH 5 - 6: MES
pH 7-8: HEPES
pH 9: AMPSO
pH 10 - 13: CAPS - Estimation method (if used):
- Not applicable.
- Details on test conditions:
- - Used chelates: HJB/Fe3+, HBED/Fe3+, o,o-EDDHA/Fe3+ and o,p-EDDHA/Fe3+
- Preparation of iron chelate solutions: Fe was added asFe(NO3)3 x 9H2O (5 % in excess respect to the chelating agent), followed by slow addition to a chelating agent solution, maintaining the pH between 6.0 and 8.0 by adding NaOH or HCl. The solution was left overnight and filtered through 0.45μm membranes.
- Test procedures: 1 mL of each solution, 4 mL of 0,125 M CaCl2, and 4 mL of a biological buffer were added to a 50-mL beaker. Then, 30 mL of water were added and the pH adjusted to: 2.0, 3.0, 4.0, 5.0, 6.0, 7.0, 8.0, 9.0, 10.0, 10.5,11.0, 11.5, 12.0, 12.5 and 13.0, either with HCl or NaOH solutions as it was needed. Each sample was transferred to a 50 mL volumetric flask, diluted to the mark with water and transferred to a plastic vessel. Solutions were shaken at 25 ºC for 3 days in darkness. At the end of this period pH values and total soluble iron were assessed by AAs. - Number of replicates:
- None.
- Positive controls:
- not specified
- Remarks:
- Not applicable.
- Negative controls:
- not specified
- Remarks:
- Not applicable.
- Statistical methods:
- No details available.
- Preliminary study:
- No preliminary study performed.
- Test performance:
- Neither unusual observations nor deviations from test procedure which will affect the obtained results are reported.
- Transformation products:
- not specified
- Details on hydrolysis and appearance of transformation product(s):
- Not applicable.
- Remarks on result:
- not measured/tested
- Other kinetic parameters:
- No other kinetic parameters are reported.
- Details on results:
- HJB/Fe3+ led to iron complexes more stable than o,p-EDDHA/Fe3+ but not as stable as those formed from o,o-EDDHA. HBED/Fe3+ formed extremely stable complexes. In all cases almost the total amount of soluble iron was recovered between pH 2 and 8, but above this point, the stability of the iron complexes was considerably reduced in o,p-EDDHA. Although HJB/Fe3+ showed slightly less stability than o,o-EDDHA iron chelates, the percentage of Fe in solution was 85 % at pH 11.
- Validity criteria fulfilled:
- yes
- Remarks:
- Basic scientific principles were met.
- Conclusions:
- The study report describes an chelate interaction experiment of iron chelates at different pH values. The test substance formed extremely stable complexes.
- Executive summary:
Different iron chelates, beside HBED/Fe3+ also HJB/Fe3+, o,o-EDDHA/Fe3+ and o,p-EDDHA/Fe3+ were used in an interaction experiment at different pH values (Lucena et al., 2009). Fe was added as Fe(NO3)3 x 9H2O (5 % in excess respect to the chelating agent), followed by slow addition to a chelating agent solution, maintaining the pH between 6.0 and 8.0 by adding NaOH or HCl. The solution was left overnight and filtered through 0.45μm membranes. 1 mL of each solution, 4 mL of 0,125 M CaCl2, and 4 mL of a biological buffer were added to a 50-mL beaker. Then, 30 mL of water were added and the pH adjusted to: 2.0, 3.0, 4.0, 5.0, 6.0, 7.0, 8.0, 9.0, 10.0, 10.5,11.0, 11.5, 12.0, 12.5 and 13.0, either with HCl or NaOH solutions as it was needed. Each sample was transferred to a 50 mL volumetric flask, diluted to the mark with water and transferred to a plastic vessel. Solutions were shaken at 25 ºC for 3 days in darkness. At the end of this period pH values and total soluble iron were assessed by AAs. The following results were obtained, which are in agreement with theoretical modelization: HJB/Fe3+ led to iron complexes more stable than o,p-EDDHA/Fe3+ but not as stable as those formed from o,o-EDDHA. HBED/Fe3+ formed extremely stable complexes. In all cases almost the total amount of soluble iron was recovered between pH 2 and 8, but above this point, the stability of the iron complexes was considerably reduced in o,p-EDDHA. Although HJB/Fe3+ showed slightly less stability than o,o-EDDHA iron chelates, the percentage of Fe in solution was 85 % at pH 11.
Reference
Description of key information
Iron chelate interaction experiment: The test substance formed extremely stable complexes.
Key value for chemical safety assessment
Additional information
Different iron chelates, beside HBED/Fe3+ also i.e. HJB/Fe3+, o,o-EDDHA/Fe3+ and o,p-EDDHA/Fe3+ were used in an interaction experiment at different pH values (Lucena et al., 2009). Fe was added as Fe(NO3)3 x 9H2O (5 % in excess respect to the chelating agent), followed by slow addition to a chelating agent solution, maintaining the pH between 6.0 and 8.0 by adding NaOH or HCl. The solution was left overnight and filtered through 0.45μm membranes. 1 mL of each solution, 4 mL of 0,125 M CaCl2, and 4 mL of a biological buffer were added to a 50-mL beaker. Then, 30 mL of water were added and the pH adjusted to: 2.0, 3.0, 4.0, 5.0, 6.0, 7.0, 8.0, 9.0, 10.0, 10.5,11.0, 11.5, 12.0, 12.5 and 13.0, either with HCl or NaOH solutions as it was needed. Each sample was transferred to a 50 mL volumetric flask, diluted to the mark with water and transferred to a plastic vessel. Solutions were shaken at 25 ºC for 3 days in darkness. At the end of this period pH values and total soluble iron were assessed by AAs. The following results were obtained, which are in agreement with theoretical modellling: HJB/Fe3+ led to iron complexes more stable than o,p-EDDHA/Fe3+ but not as stable as those formed from o,o-EDDHA. HBED/Fe3+ formed extremely stable complexes. In all cases almost the total amount of soluble iron was recovered between pH 2 and 8, but above this point, the stability of the iron complexes was considerably reduced in o,p-EDDHA. Although HJB/Fe3+ showed slightly less stability than o,o-EDDHA iron chelates, the percentage of Fe in solution was 85 % at pH 11.
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