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EC number: 257-036-7 | CAS number: 51181-50-1
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Additional information
DTPA-FeHNa was negative in the Ames test and in the in vitro micronucleus test using a treatment period of 4 h (with and without S9 -mix). In the in vitro micronucleus test using a treatment period of 20 h (continuous treatment without S9 -mix), DTPA-FeHNa was positive at levels >= 2000 µg/mL, inducing aneugenic but no clastogenic effects. This long treatment period together with the high concentrations of chelant may have resulted in exchange and substantial binding of essential elements such as zinc. Similar results were obtained with EDTA-FeNa and EDTA-CuNa2 (see robust summaries and read across document; section 13). Heimbach et al (2000; see also robust summary) concluded that the lack of effects by the Zn-EDTA salt in contrast to effects induced by Ca-, Na- and Mn-salts of EDTA, provided evidence that zinc is required for the initiation or continuation of DNA synthesis and maintaining cell function. As such, the significance of mutations produced by DTPA-FeHNa (and also EDTA-FeNa and EDTA-CuNa2) at non-physiological concentrations in an in vitro screening system is difficult to extrapolate for relevance to intact organisms.
Although no in vivo genotoxicity studies have been carried out with DTPA-FeHNa and HEDTA-FeNa, several in vivo genotoxicity studies are available for other EDTA-compounds such as EDTA-Na2H2. No genotoxic activity was observed (see also read across document in section 13).
Therefore, the overall findings indicate that HEDTA-FeNa will lack significant genotoxic potential under conditions that do not deplete essential trace elements required for normal cell function.
Short description of key information:
DTPA-FeHNa tested in the Salmonella Typhimurium Reverse Mutation Assay and the Eschericha Coli reverse mutation assay did not result in an increased number of revertant colonies in strains S. typhimurium strains TA 98, 100, 1535, 1537. An in vitro micronucleus test in human lympocytes did not result in an increased number of micronuclei following exposure for 4 h (with and without S9 mix), but it did following exposure for 20 h (without S9 mix). See also at Discussion.
Endpoint Conclusion: No study available
Justification for classification or non-classification
Bases on the results of several in vitro and in vivo gentoxicity tests (see also read across documrnt in section 13), it was concluded that for HEDTA-FeNa classification for genotoxicity is not warranted.
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