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EC number: 272-944-3 | CAS number: 68921-52-8
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Publication with summary of results only; comparable to guideline study with acceptable restrictions (no data on test substance purity, limited documentation)
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Evaluation of a Three-Exposure Mouse Bone Marrow Micronucleus Protocol
- Author:
- Shelby, M.D. et al.
- Year:
- 1 993
- Bibliographic source:
- Environmental and Molecular Mutagenesis 21: 160-179
- Reference Type:
- secondary source
- Title:
- Diesters Category of the Aliphatic Esters Chemicals (Test Plan and Robust Summaries for Substances in the HPV Test Plan)
- Author:
- US-EPA (American Chemistry Council's Aliphatic Esters Panel)
- Year:
- 2 010
- Bibliographic source:
- High Production Volume (HPV) Chemical Challenge Program (201-16837A and 201-16837B)
- Reference Type:
- secondary source
- Title:
- Bis(2-ethylhexyl)adipate (DEHA) CAS N°: 103-23-1
- Author:
- OECD
- Year:
- 2 000
- Bibliographic source:
- SIDS Initial Assessment Report for SIAM 10; Tokyo, Japan, 15-17 March 2000
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- (no data on test substance purity, no samples for the peripheral blood between 36 and 48 h following the final treatment were collected))
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Bis(2-ethylhexyl) adipate
- EC Number:
- 203-090-1
- EC Name:
- Bis(2-ethylhexyl) adipate
- Cas Number:
- 103-23-1
- Molecular formula:
- C22H42O4
- IUPAC Name:
- bis(2-ethylhexyl) adipate
- Details on test material:
- - Name of test material (as cited in study report): Bis(2-ethylhexyl)adipate
- Analytical purity: no data
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- B6C3F1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: National Toxicology Program production facility at Taconic Farms
- Age at study initiation: 9 - 14 weeks
- Weight at study initiation: 25 - 33 g
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- corn oil
- Duration of treatment / exposure:
- 3 days
- Frequency of treatment:
- one injection (0.4 mL) per day (3 treatments)
- Post exposure period:
- 24 h after the last treatment
Doses / concentrations
- Remarks:
- Doses / Concentrations:
375, 750, 1500 and 2000 mg/kg bw/day
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5 males (dose groups and negative control)
40 males (positive control)
70 males (vehicle control) - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- 7,12-dimethylbenzanthracene (DMBA) in corn oil
The following substances were used to develop the test protocol:
7,12-dimethylbenzanthracene; mitomycin C; benzidine
- Justification for choice of positive control(s): 7,12-dimethylbenzanthracene is slowly absorbed and metabolized; benzidine is an in vivo micronucleus inducer that is difficult to detect; mitomycin C is water soluble, direct acting and has an in vivo half live < 1h.
A protocol of 3 daily treatments (intraperitoneal injections) and a single sample time at 24 h following the final treatment was found to be the most effective for detecting all 3 postive control substances.
Examinations
- Tissues and cell types examined:
- Tissue: bone marrow
Cell type: erythrocytes - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Dose determination study: The selection of the maximum doses for the MN induction was based on either mortality, administration characteristics, depression in the percentage of bone marrow PCE (no less than 15% of the erythrocytes), or on the arbitrary maximum dose of 2000 mg/kg bw/day. Groups of 5 mice were administered the test stubstances by ip injection on three consecutive days at 200, 1000 and 2000 mg/kg bw. Animals were monitored twice daily, and 48 h after the last treatment, the surviving mice wer killed and bone marrow and peripheral blood smears (2 slides/tissue/mouse) were prepared. Based on the percentage of PCE among 200 erythrocytes, the maximum adminstration dose was estimated. As no evidence of toxicity at the daily dose of 2000 mg/kg bw/day was observed, this was the highest dose used in the main MN test.
TREATMENT AND SAMPLING TIMES: Groups of 5 mice were injected ip on 3 consecutive days with the test substance or the corresponding controls. Mice were euthanized with CO2 24 h after the third treatment.
DETAILS OF SLIDE PREPARATION: Bone marrow smears (2 slides per mouse) were prepared, fixed in absolute methanol, and stained with acridine orange.
METHOD OF ANALYSIS: Slides were evaluated at 1000x magnification for the number of MN-PCE among 2000 PCE and for the percentage of PCE among 200 erythrocytes. - Evaluation criteria:
- Conclusions are based on the statistical analysis of trend and of pairwise comparisons of the solvent control with individual doses and the absolute increase in MN-PCE frequency.
- Statistics:
- The data were analyzed using the Micronucleus Assay Data Management and Statistical software package. The level of signifcance was set at an alpha level of 0.05. To determine whether a specific treatment resulted in a significant increase in MN-PCE , the number of MN-PCE were pooled within each dose group and analyzed by a one-tailed trend test. In the software package used, the trend test incorporates a variance inflation factor to account for excess animal variablity. The %PCE data were analyzed by an anylsis of variance (ANOVA) test based on pooled data. Pairwise comparisons between each group and the concurrent solvent control group was by an unadjusted one-tailed Pearson chi-squared test which incorporated the calculated variance inflation factor for the study.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
Table 1. Result of the mouse bone marrow micronucleus test
Dose (mg/kg bw) |
MN-PCE/1000a)(No. of animals) |
Survival |
% PCEb) |
Corn oil (vehicle control) |
2.12 ± 0.70 |
(14 groups) |
Range: 1.1-3.7 |
0 (negative control) |
2.5 ± 0.41 (4) |
4/5 |
64.4 |
375 |
3.4 ± 0.81 (5) |
5/5 |
39.5 |
750 |
2.3 ± 0.30 (5) |
5/5 |
59.0 |
1500 |
2.4 ± 0.51 (5) |
5/5 |
60.2 |
2000 |
2.6 ± 0.58 (5) |
5/5 |
47.2 |
DMBA |
7.93 ± 1.69 |
(8 groups) |
Range: 4.4-10.6 |
a)Micronucleated PCEs per 1000 PCE scored
b)Percentage of erythrocytes that were polychromatic
DMBA = dimethylbenzanthracene (12.5 mg/kg bw/day)
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
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