Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 239-407-5 | CAS number: 15375-84-5
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Endpoint summary
Administrative data
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
An Ames test, an in vitro micronucleus test and a MLA were carried out with EDTA-MnNa2.
Link to relevant study records
- Endpoint:
- in vitro cytogenicity / micronucleus study
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Between September and December 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well conducted study under GLP
- Qualifier:
- according to guideline
- Guideline:
- other: Draft OECD Guideline 487, December 2007
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- in vitro mammalian cell micronucleus test
- Target gene:
- Formation of small membrane-bound DNA fragments such as micronuclei (chromosome aberrations); this test may detect both clastogenic and aneugenic chemicals.
- Species / strain / cell type:
- lymphocytes: human
- Details on mammalian cell type (if applicable):
- - Type and identity of media: 0.5 ml whole blood from young healthy male non-smoking individuals in RPMI-1640 with Glutamax-1, foetal calf serum, penicillin, streptomycin, phytohaemagglutinin
- Properly maintained: yes
- Periodically checked for Mycoplasma contamination: not applicable
- Periodically checked for karyotype stability: not applicable
- Periodically "cleansed" against high spontaneous background: not applicable - Additional strain / cell type characteristics:
- not applicable
- Metabolic activation:
- with and without
- Metabolic activation system:
- Aroclor 1254 induced rat liver S9 mix
- Test concentrations with justification for top dose:
- with and without S9 mix: 0, 125, 250, 500, 1000, 2000 and 3891 µg/ml (4 h treatment & 20 h recovery)
without S9 mix: 0, 1000, 1500, 2000, 2500, 3000 and 3891 µg/ml (20 h treatment & 28 h recovery)
3891 µg/ml corresponds to 10 mmol/L - Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: culture medium (supplemented RPMI 1640)
- Justification for choice of solvent/vehicle: good water solubility - Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: cyclophosphamide (with S9-mix; 4 h treatment), mitomycine C and vinblastine sulphate (without S9-mix; 4 h and 20 h treatment)
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in medium
DURATION
- Preincubation period: cultures were set up within 1 h after blood withdrawal, incubated for 48 h
- Exposure duration: 4 h (with and without S9-mix), 20 h (without S9-mix)
- Expression time (cells in growth medium): 48 h preincubation + 4 h exposure + 20 h recovery = 72 h in total, and
48 h preincubation + 20 h exposure + 28 h recovery = 96 h in total
- Selection time (if incubation with a selection agent): not applicable
- Fixation time (start of exposure up to fixation or harvest of cells): in case of 4-h exposures, cells were harvested and slides were fixed 20 h later; in case of 20 h exposure, cells were harvested and slides were fixed 28 h later
SELECTION AGENT (mutation assays): not applicable
SPINDLE INHIBITOR (cytogenetic assays): not applicable
STAIN (for cytogenetic assays): acridin-orange
NUMBER OF REPLICATIONS: 3 sides per concentration (1 for CBP index (cytotoxicity), and 2 for micronucleus formation)
NUMBER OF CELLS EVALUATED: 500 per slide, thus 1000 per culture
DETERMINATION OF CYTOTOXICITY
- Method: by using CBP index = (1x no. of mononucleates + 2x no. of binucleates + 3x no. of multinucleates) / total number of cells
Replication index (%) = (CBPI ^ T(mean) -1 / CPBI ^ C(mean) -1) x 100
Cytotoxicity (%) = 100 - replication index
with T(mean) = mean of 2 test cultures and C(mean) = mean of 2 control cultures
OTHER EXAMINATIONS: none - Evaluation criteria:
- The study was considered valid because the selected clastogenic and aneugenic positive controls gave a statistically significantly increase in the number of binucleated cells containing micronuclei and the negative controls were within the historical data presented by test facility and in the literature (E. Lorge et al, 2006).
A response was considered to be positive if a statistically significant concentration-related or a reproducible statistically significant increase in the number of binucleated cells containing micronuclei was induced, at any of the test points.
A response was considered to be equivocal if the percentage of binucleated cells containing micronuclei was statistically marginal higher than that of the negative control (<= 0.05A test substance was considered to be negative if it produces neither a statistically significant concentration-related or reproducible statistically significant increase in the number of binucleated cells containing micronuclei, at any of the test points (p>0.1).
The statistical method was used as an aid in evaluating the test results but was not the only determining factor for a positive response. Both statistical methods and biological relevance of the test results were considered together in the evaluation. - Statistics:
- The frequencies of micronuclei found in the cultures treated with the test substance and positive control cultures were compared with those of the concurrent solvent control using Fisher's exact probability test (one-sided). The results were considered statistically significant when the p-value of the Fisher's exact probability test was <= 0.05.
- Species / strain:
- lymphocytes: human
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- other: yes, only at the highest levels tested
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
- Effects of pH: no (measured)
- Effects of osmolality: no (measured)
- Evaporation from medium: no (test substance is not volatile)
- Water solubility: no (good water solubility)
- Precipitation: no
- Other confounding effects: none
RANGE-FINDING/SCREENING STUDIES: not done
COMPARISON WITH HISTORICAL CONTROL DATA: yes
ADDITIONAL INFORMATION ON CYTOTOXICITY: none - Conclusions:
- Interpretation of results (migrated information):
negative
It is conluded that EDTA-MnNa2 under the conditions of this test was neither clastogenic nor aneugenic to cultured human lymphocytes. - Executive summary:
The test substance EDTA-MnNa2 was examined for its potential to induce micronuclei in cultured binucleated human lymphocytes, in both the absence and presence of a metabolic activation system (S9-mix) with duplicate cultures. Two separate in vitro micronucleus tests were conducted for which blood was obtained from two different donors. In the first test, in the presence and absence of S9 -mix, the treatment/recovery time was 4/20 hours (pulse treatment method). In the second test, concentration spacing was modified and the treatment/recovery times were 20/28 hours (continuous treatment) in the absence of S9-mix. Dose levels, ranging from 7.8 to 3891 µg/ml, were tested. In all instances, the maximum final concentration in the culture medium was 10 mmol/l. A purity of 92.3% was taken into account while preparing the dosing solutions. Culture medium was used as solvent for the test substance. Cytotoxicity was calculated from the Cytokinesis-Block Proliferation Index (CBPI). Cyclophosphamide, a clastogenic compound which requires metabolic activation, was used as positive control in the presence of S9-mix. A known clastogenic compound (Mitomycin C) and a known aneugenic compound (Vinblastine sulphate) were used as positive controls in the absence of S9-mix.
In the first test, in the presence and absence of S9-mix, the highest dose level (3891 µg/ml) was cytoxic to the cells based on the CBPI. Analysis of micronuclei formation was carried out in the cultures of three dose levels (1000, 2000 and 3891 µg/ml) of the test substance, the cultures of the solvent control and the cultures of the positive controls. In the first test, the test substance did not induce a statistically significant increase in the number of binucleated cells containing micronuclei.
In the second test, the two highest dose levels (3000 and 3891 pg/ml) were cytotoxic to the cells based on the CBPI. Analysis of micronuclei formation was carried out in the cultures of three dose levels (2500, 3000 and 3891 µg/ml) of the test substance, the cultures of the solvent control and the cultures of the positive controls. In the second test, the test substance did not induce a statistically significant increase in the number of binucleated cells containing micronuclei.
Treatment with the positive controls Cyclophosphamide, Vinblastine sulphate and Mitomycin C resulted in statistically significant increases in the numbers of binucleated cells containing micronuclei, when compared to the numbers observed in the cultures treated with the solvent control. This demonstrates the validity of the study. From the results obtained in two in vitro micronucleus tests it is concluded that, under the conditions used in this study, the test substance EDTA-MnNa2 was neither clastogenic nor aneugenic to cultured human lymphocytes.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
Additional information from genetic toxicity in vitro:
Because the Ames test, the in vitro micronucleus test in cultured human lymphocytes and the MLA were negative, it was concluded that EDTA-MnNa2 is not mutagenic and that no in vivo tests are needed. In addition, several genotoxicity studies are available for other EDTA-compounds such as EDTA-Na2H2, EDTA-Na3H and several metal-chelates. None of these showed genotoxic activity (see also read across document in section 13).
Justification for selection of genetic toxicity endpoint
This is one of the three in vitro gentox studies carried out with EDTA-MnNa2; all three studies were negative.
Justification for classification or non-classification
Because both the Ames test, the in vitro micronucleus test and the MLA were negative, it was conluded that EDTA-MnNa2 is not mutagenic and that no classification is needed for this endpoint.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
![ECHA](/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/echa_logo.png)