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EC number: 400-660-3 | CAS number: 111687-36-6 AMMONIUM-EISEN-PDTA; AMMONIUM-IRON-PDTA; COMPLEX OF CHELATING AGENT NO. 1; DISSOLVINE FD-FE-14; DISSOLVINE PD-FE-14; PDTA-FN; RAZ; SEL COMPLEXE D'AGENT CHELATANT KODAK NO. 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
Results of the Ames test and the in vivo micronucleus test were negative; the results of the in vitro CA test were ambiguous. In the latter test, PDTA-FeNH4 showed some evidence of clastogenic activity in the absence of S-9 mix, but only at a single, toxic concentration. At this same concentration, there were indications of an effect of PDTA-FeNH4 on spindle formation or function. There was also limited evidence of weak clastogenic activity in the presence of S-9 mix, but again only at the highest concentration tested.
The long treatment period together with the high concentration of the chelant may have resulted in exchange and substantial binding of essential elements such as zinc. Heimbach et al (2000; see 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 EDTA-FeNa (see Heimbach et al., 2000) and PDTA-FeNH4 (this study) at non-physiological concentrations in an in vitro screening system is difficult to extrapolate for relevance to intact organisms.
Therefore, the overall findings indicate that PDTA-FeNH4 lacks significant genotoxic potential under conditions that do not deplete essential trace elements required for normal cell function.
Short description of key information:
The following studies are available: Ames test, in vitro chromosome aberration test and an in vivo mouse micronucleus test.
Endpoint Conclusion:
Justification for classification or non-classification
The test substance gave negative results in one in vitro mutagenicity test, viz. the Ames test, and in one in vivo mutagenicity test, viz. the micronucleus test. It gave ambiguous results in the in vitro chromosome aberration test (at a high, cytotoxic concentration). The latter was most probably explained by induction of Zn deficiency. Overall, it was concluded that classification for genotoxicity is not warranted.
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