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Diss Factsheets
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EC number: 200-449-4 | CAS number: 60-00-4
- 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
Phototransformation in soil
Administrative data
Link to relevant study record(s)
- Endpoint:
- phototransformation in soil
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Principles of method if other than guideline:
- Method: other (measured)
- GLP compliance:
- no
- Specific details on test material used for the study:
- RADIOLABELLING INFORMATION
14C-Carboxyl-EDTA 97 % (2.54 mCi/mM)
14C-Acetate-2-EDTA 98 % (1.36 mCi/mM) - Radiolabelling:
- yes
- Light source:
- other: sunlight or UV light (254 nm)
- Details on test conditions:
- To examine the effect of light on degradation, 14C-acetate-2-EDTA was freshly dissolved in deionized, glass-distilled water, neutralized and stored in an aluminium foil-wrapped flask at 2 °C. This substrate was added to Spinks soil, four of which were wrapped with aluminium foil and incubated in the dark, and the four remaining were incubated in the light. 14CO2 production was measured weekly for 7 weeks.
After four weeks one light- and one dark-incubated flask were extracted with water; and the extract analyzed by 14C-TLC and autoradiography.
In a related experiment portions of an aqueous solution of the Fe(III)-chelate of 14C-carboxyl-EDTA were exposed to 5 hours of sunlight or 5 hours of UV light (254 nm). The resulting photodegradation mixture as well as unexposed chelate were incubated in Spinks soil. - Key result
- % Degr.:
- 71
- Sampling time:
- 5 h
Reference
The sensitivity of Fe(III)-EDTA to sunlight
and UV light was apparent since 60.9 and 15.1 %,
respectively, of the carboxyl label was mineralized by
these treatments. When the remaining EDTA and photolysis products
were incubated with soil, initial rapid mineralization occurred, particularly
when no organic matter was added. This suggests that certain components
of the photolysis mixture are more readily biodegradable than EDTA.
In the case of the sunlight pretreatment, approx. 86.5 % of the carboxyl
groups were volatilized by the combined photo- and biocatalysis.
Description of key information
Key value for chemical safety assessment
Additional information
As phototransformation in soil is not a standard information requirement according to Regulation (EC) No. 1907/2006 and there is no indication from the Chemical Safety Assessment according to Annex I on the need to investigate further the fate and behavior of the substance (Annex X requirement), no further testing is considered necessary. Available supporting data for subcategory 1 members indicate that some EDTA species, especially iron complexes, are to a certain degree photolysable.
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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